MORPHOLOGIC COMPARISONS OF SHALLOW AND DEEPWATER BENTHIC MARINE DIATOMS OF ONSLOW BAY, NORTH CAROLINA
Dorien Kymberly McGee
A Thesis Submitted to the University of North Carolina at Wilmington in Partial Fulfillment Of the Requirements for the Degree of Master of Science
Department of Earth Sciences
University of North Carolina at Wilmington
2005
Approved by
Advisory Committee
______Patricia Kelley______Lawrence Cahoon______
______Richard Laws______Chair
Accepted By
______Dean, Graduate School This thesis has been prepared in a style and format
Consistent with the journal
Diatom Research
ii TABLE OF CONTENTS
ABSTRACT...... v
ACKNOWLEDGMENTS ...... vii
DEDICATION...... viii
LIST OF TABLES...... ix
LIST OF FIGURES ...... x
INTRODUCTION ...... 1
Overview...... 1
Diatom Biology...... 2
Previous Work ...... 4
Hypothesis...... 11
METHODS ...... 13
Sample Collection...... 13
Sample Preparation ...... 17
Microscope Analysis...... 19
Quantitative/Morphometric Analysis...... 21
RESULTS ...... 28
Deepwater Locality: Onslow Bay...... 28
Transect 1...... 32
Transect 2...... 33
Shallow water Locality: Masonboro Island ...... 37
Station DET I-B ...... 39
iii Station ND IV-D...... 41
Deepwater/Shallow water Comparison...... 43
DISCUSSION...... 50
External Morphology...... 52
Physiology...... 54
Implications...... 55
CONCLUSIONS...... 58
LITERATURE CITED ...... 60
APPENDICES ...... 65
iv ABSTRACT
In October 2003, in-situ, living benthic marine diatoms were recovered from sandy
sediments from 67 m to 191 m depth in Onslow Bay, North Carolina, by a remotely operated
vehicle tethered to the R/V Cape Hatteras. Fourteen stations were sampled, with surface
incident irradiance flux ranging from 3.740% of the surface irradiance at the shallowest station to
0.028% at the deepest. Attenuation coefficients fluctuated with depth, averaging between 0.0443
(4.43% loss per meter) and 0.0842 (8.42% loss per meter). Bottom temperatures decreased with
depth from 25.3 °C to 14.9°C. One hundred twenty-six species of 29 genera were identified
from cleaned sediments from all 14 stations. Eleven live species from six genera were
documented as live and identified from the shallowest and deepest of the fourteen stations
(Actinoptychus splendens, Amphora coffeaformis, Cocconeis disculus, Cocconeis distans,
Cocconeis placentula, Diploneis chersonensis, Navicula Sp. a, Navicula digitoconvergens,
Nitschia frustulum, Nitschia pellucida, and Nitschia panduriformis), and analyzed morphometrically based on apical and transapical axis lengths, degree of frustal ornamentation, and surface area to volume ratios. These data were then compared to those for shallow water samples previously collected from intertidal marsh sediments on Masonboro Island, North
Carolina. Though apical axis lengths were significantly larger in the shallow water samples
(p = 8.6 x 10-6), transapical axis lengths and degree of ornamentation did not differ significantly
between deepwater and shallow water regions. Surface area to volume ratios of three out of five
live species found in both shallow water and deepwater were significantly lower in the deepwater
stations (p = 0.00045 to 0.0088), indicating that differences in shape may affect the efficiency of
light collection. The results of this study indicate taxonomic diversity and variety of frustal
v morphology of benthic marine diatoms are greater shallow water; however, the presence of these microalgae in the deeper sediments of Onslow Bay may have far-reaching impacts on nutrient cycling and food web dynamics on the shelf and upper slope.
vi ACKNOWLEDGMENTS
I would like to thank UNCW’s Center for Marine Science, the Department of Earth
Sciences, the UNCW Graduate School, and the National Oceanic and Atmospheric
Administration’s National Undersea Research Program for their financial support during the
completion of this degree.
I would also like to thank my committee members, Richard Laws, Larry Cahoon, and
Patricia Kelley for their unwavering support and guidance in this project. I am indebted to them
for the time, energy, and assistance they have provided over the past two years. Much
appreciation is also extended to the Duke University/University of North Carolina
Oceanographic Consortium for their use of the Research Vessel Cape Hatteras and its crew in
collecting field samples in Onslow Bay and making our stay as enjoyable as nature would allow.
I would like to thank Lance Horn of NOAA’s National Undersea Research Center, UNCW’s
Coastal Ocean Research and Monitoring Program and Aquatic Ecology Lab for their technical
assistance. Much gratitude is also extended to Cathy Morris and Anne Sutter for their logistical
support.
The journey for answers is often more fulfilling than the answers themselves. Much love
and thanks to those friends who’ve taught me about myself along the way: the DeLoach and
CMS clan, the San Sal crew, and to Annie, Twinks, Rociel, Lisa F., and Lisa B, and Scott.
Thanks to Steffi for the moral support and for showing me how to be strong in the face of
opposition; to Greg for the wisdom and understanding, and for being there unconditionally; and
last but not least, to my best friend Micól, with whom I’ve learned to be effortlessly, live happy,
and enjoy the champagne highs.
vii DEDICATION
This thesis is dedicated to my family: To my Mom, who taught me how to persevere with
grace; to my Aunt Gail for showing me what a little determination could accomplish; to Uncle
Jim for being my geological muse; to Sarah, Matt, Luke, Uncle Jack, and Aunt Lynn for their support (despite the rock jokes); and the zoo crew Jasmine, Maako, Saba, Minerva, Rasta, and
Inca, as well as Tommy, Gandalf, and Julep (who didn’t see the completion of this project but
aided me in getting there nonetheless).
viii LIST OF TABLES
Table Page
1. Station 1 taxonomic composition and morphometrics...... 34
2. Station 14 taxonomic composition and morphometrics...... 36
3. Deepwater mean surface area to volume ratios by species...... 38
4. Station DET I-B taxonomic composition and morphometrics ...... 40
5. Station ND IV-D taxonomic composition and morphometrics ...... 42
6. Shallow water mean surface area to volume ratios by species ...... 44
7. Morphometric analysis of 400 shallow water valves versus morphometric analysis of a subset of 259 randomly selected valves of the same sample...... 45
8. Deepwater/shallow water morphometric comparison using same sample sizes ...... 46
9. ANOVA results for deepwater versus shallow water physiological and S/V ratio parameters...... 48
ix
LIST OF FIGURES
Figure Page
1. a) Valve and girdle views of Biddulphia sp...... 3 b) Valve view of the solitary pennate diatom Navicula salinarum ...... 3 c) Girdle view of the colonial centric diatom Paralia sulcata...... 3
2. a) Onslow Bay and Masonboro sample collection locations...... 14 b) Transect 1 ...... 15 c) Transect 2...... 15
3. a) ROV Phantom S2...... 16 b) Tri-Scoop 1000 sediment scoop ...... 16 c) Seabird SBE 911plus CTD rosette...... 16
4. Masonboro Island, North Carolina sample locations...... 20
5. a) Division of diatom frustule into sectors...... 23 b) Radial discoid symmetry ...... 23 c) Radial cylindrical symmetry...... 23 d) Bilateral symmetry, biraphid ...... 23 e) Bilateral symmetry, monoraphid ...... 23 f) Bilateral symmetry, araphid ...... 23 g) Hyaline ornamentation, Index 1 ...... 23 h) Hyaline to complex ornamentation, Index 2 ...... 23 i) Complex ornamentation, Index 3 ...... 23 j)Striae-dominant, unoccluded areolae ...... 24 k)Striae-dominant occluded areolae, rotae ...... 24 l) Striae-dominant occluded areolae, cribera ...... 24 m) Striae-dominant occluded areolae, volae...... 24 n) Striae-dominant, occluded areolae, hymenes ...... 24 o) Sterna-dominant...... 24 p) Multiple ornamentation ...... 24
6. a) Transect 1 percent surface incident irradiation at the bottom of the water column...... 29 b) Transect 2 percent surface incident irradiation at the bottom of the water column ...... 29
7. a) Transect 1 attenuation coefficients ...... 30 b) Transect 2 attenuation coefficients...... 30
8. a) Transect 1 surface and bottom temperatures ...... 31 b) Transect 2 surface and bottom temperatures ...... 31
x INTRODUCTION
Overview
Benthic marine diatoms live in a variety of environments ranging from marshes to the
outer continental shelf. Due to their photosynthetic nature, the primary limiting factor governing
their distribution is light availability. Distribution of benthic diatoms should therefore be light-
limited. To date, the maximum depth at which live benthic marine diatoms have been found is
83 m, off the coast of Madagascar (Plant-Cuny, 1978). However, during a recent research cruise
aboard the R/V Cape Hatteras, live benthic diatoms were found at the continental shelf-break
region of Onslow Bay, North Carolina, at depths up to 191 m, the lower limit of the photic zone
of open water (~200 m). Benthic diatoms have been previously documented living in-situ in
sediments in Onslow Bay at depths of 63 m (Cahoon et al. 1992; Cahoon and Laws, 1993);
therefore, physical transport of these frustules via currents and wave energy from shallower
regions to this depth is unlikely. Though the possibility of physical transport of diatoms beyond
the
63 m depth cannot be eliminated, there are several lines of reason suggesting their in-situ growth
at the depths sampled in this study. First, the distance from land (>50 km) and virtual absence of
planktonic and tychopelagic species from the sample sediments reduces the likelihood of
transport from shore or settling from surface waters, where such species are common. Second,
wave energy and strong currents rarely reach these depths except during strong storms and
hurricanes, thus keeping sediment transport in these regions to a minimum. Third, live species
were found continuously at each of the fourteen stations sampled as opposed to being found in
patches, lessening the likelihood that transport is occurring at depth. The absence of warmer
bottom water temperatures in the deeper of stations sampled in Onslow Bay (such as those recorded in the shallower of these stations) also suggests that transport is not occurring between stations.
The purpose of this project is to compare species composition and morphologies of
benthic marine diatoms of the continental shelf to those of the back-barrier marsh zone of
Onslow Bay, North Carolina, using light and scanning electron microscopy in order to determine what, if any, differences exist between the assemblages from these contrasting habitats.
Diatom Biology
Diatoms are single-celled marine and freshwater microalgae encased in a heterovalvar, siliceous shell called the frustule (Figure 1). The larger of the two valves, the epitheca, fits over the smaller valve, the hypotheca, and the two are held together by a girdle band. Frustules range in size from 1 micron to 1 millimeter, can be simple to ornate in structure, and have frustule morphologies loosely reflecting their life habitat. Forms are usually classified as centric or pennate. Centric diatoms are radially symmetric and may have a discoid or cylindrical shape and are typically planktonic, but may also adhere to substrates. Pennate diatoms are usually solitary, are bilaterally symmetrical, and elongate in shape. Pennates may have one or more raphe, or valve slit, running the length of the frustule. Monoraphid diatoms such as the genus Cocconeis have one raphe on the hypothecal valve, while biraphid diatoms such as the genus Navicula have a raphe on both valves. Raphes are believed to secrete a mucilaginous layer, allowing diatoms to adhere and move on a chosen substratum. Hence most raphid diatoms are considered to be benthic.
2
a. b. epitheca
Valve raphe
frustule
hypotheca Girdle
frustul epitheca c.
girdle
hypotheca
2 cells
Figure 1. a) Valve and girdle views of Biddulphia sp. (by Denise Eaton). b) Valve view of the solitary pennate diatom Navicula salinarum. c) Girdle view of the colonial centric diatom Paralia sulcata.
3 Previous Work
Frequent taxonomic reorganization of diatoms leaves a confused trail of classification
schemes, though the Round et al. (1990) classification is the commonly utilized system.
Diatoms compose the division Bacillariophyta and include three classes based on frustule
structure: Coscinodiscophyceae (centric forms), Fragilariophyceae (araphid pennate forms), and
Bacillariophyceae (raphid pennate forms). Round et al. (1990) provides the most complete and
detailed reference for distinguishing genera based on morphological characteristics, as revealed
by light and scanning electron microscopy. This reference also includes an extensive
introduction highlighting diatom morphology and biological processes. A more complete biological description of diatoms can be found in Werner (1977). Differentiation at the species level relies upon the descriptions and light microscopy of numerous authors. Cleve-Euler
(1952), Hustedt (1977), and John (1983) each provide extensive morphological and life-mode descriptions accompanied by detailed species-level photographs and line drawings. Hartley
(1996) includes hundreds of line drawings of species, but does not provide descriptions.
Hustedt (1955) pioneered the characterization of marine diatoms native to the North
Carolina coast by examining mud samples previously collected by Dr. Harold Humm of the
Duke University Marine Laboratory. These samples originated from littoral muds at the beach and in the harbor of Beaufort and contained numerous novel species that until that time had not been described. Marshall (1982) characterized the composition of phytoplankton in this region by identifying taxa from surface-water samples collected along a 600 mile stretch of coastline from Cape Lookout, North Carolina, to Cape Canaveral, Florida, during fall cruises in 1973 and
1978. Ninety-one stations were sampled total, ranging in depths from 9 m on the upper shelf to
318 m near the slope. Depths at 35 of these stations were less than 35 m, 45 stations were
4 between 44 m and 200 m, and 4 stations were deeper than 200 m. Taxonomic groups and their
constituent species were identified and sorted based on their distance from shore (<35 km from
shore being near shore, >35 km from shore being far shore). Concentrations were measured in
number of individuals per liter, and the average number of taxonomic groups and their
concentrations were slightly higher in near shore areas. Diatoms were one of five dominant
taxonomic groups and included 194 total species. Fifty-six percent of these species existed in
near shore and far shore areas, 17% were found in near shore areas only, and the remaining 27%
were found in far shore areas only. Stations closer to shore had higher concentrations of larger centric diatom forms; however, most near shore individuals were smaller than far shore individuals.
Cahoon et al. (1992, 1993) furthered diatom research for the North Carolina area and began characterizing modern benthic assemblages of species living on inner to slope regions of
Onslow Bay. They found that planktonic species of this region were often centric in form, though some centric species may be tychopelagic (benthic dwellers dislodged and temporarily suspended). Most benthic species were pennate in form and classed as epipsammic (living on sand grains) or epilithic (living on hard bottom). The differing assemblages between planktonic and benthic environments suggested the benthic colonies were established and not displaced from other environments. Benthic communities engaging in active photosynthesis were documented to depths of 63 m, with high fucoxanthin: chlorophyll a ratios, indicating either a fucoxanthin-rich community or an adaptive strategy to lower wavelengths (400-550 nm).
Chlorophyll a was also documented in decreasing quantities from sediment samples at depths up to 222 m. Because light flux calculations and pigment data for North Carolina coastal waters indicated that benthic species may live at depths up to 90 m, it was hypothesized that microalgae
5 in deeper areas may be inactive, perhaps shifting into resting spore stages. It was noted,
however, that a previous study by Palmisano et al. (1985) documented active benthic diatom
cells at approximately 110 m in Antarctica.
Cahoon (1999) synthesized data from a variety of resources in a meta-analysis assessing
the biases of benthic microalgal production and the function of benthic microalgae in the
relatively unstudied regions of the neritic zone (i.e. continental shelf ecosystems). Estimates of
production by benthic microalgae are likely skewed as sampling is biased both by geography and depth, with the majority of research taking place in shallow coastal waters of temperate regions and in areas where funding for such research is available (i.e. east and west coasts of the United
States and Canada, and the western coasts of Europe). Furthermore, the variety of techniques used in measuring chlorophyll a, as well as the differing concentrations of chlorophyll a between
light- and shade-adapted species, likely lead to estimates of production that are somewhat
removed from actual values. Though minimum light intensity data are scarce, they clearly
indicate that benthic microalgae are capable of living in conditions where irradiance and surface
incident radiation is lower than traditionally accepted values. A study by Falkowski (1988) cited in this paper, reduces the average light compensation value for algal growth from 1% to 0.1%
surface incident radiation. Because oligotrophic waters are generally clearer than coastal waters,
compensation values of 0.1% with 0.07% attenuation per meter would yield compensation
-kd depths of 100 m based on the equation ID = I0e , where ID equals irradiance at a certain depth D,
I0 equals irradiance at the surface, and kd equals the extinction coefficient at depth D. Because
benthic microalgae are more concentrated at the sediment-water interface than in the water column, extracellular polymeric substances (mucilage) tend to accumulate, which increase stabilization of the sediments and benefit the species by minimizing turbidity and resuspension.
6 Their position at the sediment-water interface also places benthic microalgae at the “gate” of nutrient transport both in and out of the sediments, making it highly likely that nutrient and other biochemical concentrations are altered by their presence. Finally, benthic microalgae are known food sources for a variety of grazers from zooplankton to bivalves and crabs, implying that ranges of grazers may be wider should benthic microalgae distribution be underestimated.
Hudson and Legendre (1987) studied the morphologies of five species of diatoms native to Point Mitis and Baie des Sables, Quebec, to characterize their ecologic implications. Based on differences in form, mobility, solitary or colonial growth preferences, and position on the sediment surface (prostrate/parallel to the bottom versus erect, or extending into the water column), each species was expected to be distinct in behavior and niche occupation. Using five species of diatoms (a raphid and non-raphid colonial, non-mobile species; two raphid non- colonial slow-moving species; and one raphid non-colonial fast-moving species), distribution and settling analyses took place by studying their individual aggregation patterns and mobility both in a natural setting and under laboratory conditions. As the number of individuals overall increased, non-mobile and slow-moving species tended to aggregate in increasingly fewer patches with high concentrations of cells. At the same time, faster-moving species displayed the opposite behavior, aggregating in numerous patches of lower concentrations of cells. Because the distributions were correlated to the speed of the movement of the species, the life habit of the species (colonial or solitary) and the presence of a raphe did not seem to impact the results.
Likewise, the similar distributions between non-mobile and slow-moving species indicated that movement as a whole for this group did not appear to be advantageous. Though mobility would appear to be useful in maintaining an orientation towards a light source, it was implied that either slow-moving species may not be able to move at a rate sufficient enough to be advantageous
7 under these circumstances, or that they were not limited by light availability. Furthermore, colonial diatom species tended to be larger in size than solitary species, reducing their surface- area-to-volume ratio and making them less efficient at light absorption. This feature would require a more upright posture in the water column, effectively increasing their risk of predation by grazers. The collective ecological implications from these results indicate that simply extrapolating behavior and niche occupation by valve morphology alone is insufficient, and that species of various growth forms can coexist in the same niche due to a more complex set of behavioral variables.
Kudo et al. (2000) quantified the effects of temperature and iron supply on the growth rates of the marine planktonic diatom Phaeodactylum tricornutum. Cell cultures were grown in artificial seawater under various temperatures and were either supplied with iron manually or made dependent on trace amounts of iron from the seawater. Iron-replete and depleted cells both grew best at 20 °C. Their growth rates decreased gradually below this temperature and decreased sharply above. Iron-depleted cells grew at half the rate of iron-replete cells at 20 °C, and at less than half the rate below 20 °C. These results specifically defined and supported more general observations of the same phenomenon by the authors. An increase in temperature leads to an increase in metabolism to an optimum level, after which the cost of high metabolic activity
(respiration) outweighs the benefits (growth rate). Plant metabolism, including photosynthesis, nitrate assimilation, and respiratory electron transport, is highly dependent on iron.
Nayar et al. (2005) studied the effects of dredging and light attenuation on size fractionation of the planktonic diatom Skeletonema costatum. They found that the size of cells increased between high light (undredged) and low light (dredged) waters, suggesting that larger cell sizes were advantageous under low-light conditions. To test this hypothesis, light
8 experimentation took place over a four day period by mixing two samples of S. costatum, one
collected from both the surface and subsurface layers, in each of four mesocosms made from 25
L carboys floated in the surface waters of a nearby marina. Two carboys were wrapped in black
netting to reduce the light to 10% of that in the remaining two carboys, which were artificially lit
to maintain constant irradiance. Wave activity from marina traffic was used as an agitant to keep
the mesocosms evenly mixed. Daily samples were taken and filtered through progressively
smaller millipore filters to obtain size fractioning of cells. End results showed a turnover in size
fractions, with smaller sizes (2 μm – 20 μm) becoming dominant in the high-light mesocosms,
and larger sizes (20 μm – 200 μm) becoming dominant in the low-light conditions.
Werner (1977) synthesized the research of several scientists to characterize the reactions
of diatoms to various intensities and qualities of light. Adaptations to changes in light intensity
vary between species and include decreases in cell volume and chloroplast numbers at low light,
increased chlorophyll content at low light, and increases in photosynthesis rate at high light. For
example, Cyclotella nana cultured in blue, green, and white light demonstrated the highest
photosynthesis rate in blue light of any intensity due to the increase in chlorophyll a and c in the cell. Upward and downward migration cycles in the sediment by benthic diatoms also vary between species, indicating variations in tolerance for light exposure. While some species migrate up through the sediment column to the surface in morning hours and migrate downward at noon on sunny days, others remain on the surface throughout the day, migrating down only at dusk. Hopkins (1969) demonstrated that some species failed to surface at all when light intensities associated with seasonality were too high. Diatoms in that study did not surface when light intensities surpassed 650 lux in the summer and 800 lux in the winter. Finally, as red light penetrates further than blue light in turbid water and in muds (Sverdrup et al., 1942), it was
9 suggested that benthic diatoms of low latitudes with high light intensities may exhibit a higher
photosynthesis rate just below the surface, as high light intensities at the surface may inhibit
photosynthesis.
Jochem (1999) examined changes in metabolic activity of marine phytoplankton,
including diatoms, during extended periods of darkness. For ten to twelve days, batch cultures of
these phytoplankton were exposed to total darkness and sampled once daily for cytometric
analysis. Unlike the chlorophytes and most primnesiophytes in the culture, the diatoms present
in this experiment (Bacteriastrum sp. and an unidentified Nitschia-like species) showed no change in metabolic activity during the darkness exposure, and nearly all cells began rapid population growth upon re-entry into light following the experiment. This response was considered odd as the observed response of most diatoms is a reduction of metabolism or formation of resting spores when exposed to extended periods of darkness. Peters and Thomas
(1996) and Peters (1996) hypothesized that heterotrophy may allow diatoms to survive months of
darkness. Jochem reported the absence of this phenomenon in his experiment, but concluded the duration of his experiments may not have been long enough to induce a heterotrophic response.
Finally, though Bacteriastrum is a planktonic species and the habit of the Nitschia-like species is unknown, it has not been shown that this behavior cannot be attributable to benthic species.
Moisan and Mitchell (2001) hypothesized that mycosporine-like amino acids (MAAs) found in a variety of phytoplankton including diatoms, dinoflagellates, and cyanobacteria served as sunscreens, protecting them from ultraviolet-B (UV-B) radiation. Moisan and Mitchell cultured the planktonic Antarctic prymnesiophyte species Phaeocystis antarctica in f/2 medium and exposed samples of these cultures to various intensities of photosynthetically active radiation
(PAR) from a tungsten-halogen light source. They found an increase in overall concentrations of
10 MAA and a decrease in photosynthetic pigment with increasing irradiance. Because fluxes in
UV absorption lessened with an increase in MAA and because MAAs were not linked to photosynthesis, it was concluded that MAAs served as effective sunscreens for this species.
Phaeocystis antarctica would be allowed to carry on photosynthesis uninhibited during increased
light intensities of austral spring in Antarctica resulting from the presence of an ozone hole,
giving it a distinct advantage. Because MAAs are present in other phytoplankton species, the
results of this study suggest similar reactions may take place in other taxa, though the precise
role of MAAs in these taxa is as yet unknown. It may be hypothesized that the concentration of
MAAs in deepwater benthic diatom species may be less than those concentrations in shallow-
water species as UVB radiation is typically absorbed in the upper meter of water (shallower in
turbid conditions), lessening the need for MAAs as sunscreens in deepwater assemblages.
Hypothesis
My hypothesis states that external morphological features of the diatom frustule may
exert significant control on light collection and absorption, and therefore should vary between
species in higher light level shallow coastal regions versus species from the lower light level
outer-shelf regions. Species that live in the relatively deeper outer-shelf waters would be
expected to collect, absorb, and use light more efficiently than species that live in shallower
coastal areas. One possibility is that outer-shelf species may have frustal variations that enhance
their ability to absorb light (i.e., complex ornamentation, and differing frustal size and shape
compared to shallow water floras) Conversely, diatoms of the shallower back-barrier marsh
zone would have frustal variations suited to high-light habitats (simple or no ornamentation,
differing frustal size and shape compared to deepwater assemblages). Ornamental features on
11 the valve such as spines, nodules, sterna, and ocelli, can increase the surface area of the frustule, allowing more area for light absorption, and may even aid in deflecting back toward the valve surface any photons that may inadvertently have been reflected away. Variation in size and shape of the frustule may also contribute to efficiency of light absorption. Apical and transapical axes may grow proportionally larger than the pervalvar axis (thickness) as a means of increasing their surface area and taking on a discoid shape, as irradiance decreases. In this way, benthic diatoms increase the amount of surface area on the valve face, and decrease their overall frustal thickness, thereby increasing their potential for light absorption and its penetration through the frustule. Likewise, as irradiance increases, the apical and transapical axis lengths may shrink proportionately smaller than the pervalvar axis, giving the frustule a more cylindrical shape
(perhaps as safeguard against overexposure). On the other hand, the pervalvar axis may grow in proportion to apical and transapical axes as a means of increasing cell volume for housing larger chloroplasts. Therefore, some fluctuation in surface area and/or volume ratio is expected between diatoms that are light limited and those that are not. Finally, benthic species compositions should become less diverse with depth and be composed mainly of pennate forms.
If the hypothesis is rejected, community differences and frustal morphologies of shallow and deepwater species will not be significantly different despite habitat depth. Because very little is known about diatom functional morphology, this study will answer basic questions of habitat preference of benthic diatom species and differences in taxonomic composition between the assemblages from the two habitats by making possible correlations to exterior features of the frustule.
12 METHODS
Sample Collection
Bottom sediment samples were collected during a five-day cruise aboard the Duke
University/University of North Carolina Oceanographic Consortium’s research vessel R/V Cape
Hatteras on October 13-18, 2003. Samples were taken from the soft bottom sediments of 14 stations on the continental shelf-break region of Onslow Bay. These stations were arbitrarily chosen to produce two transects of increasing depth (Figure 2, Appendix A). Transect 1, sampled on October 16, 2003, included Stations 1-8 and was situated on the lower shelf near the shelf break, with depths increasing from 67.2 m to 121.0 m. Transect 2, sampled on October 17,
2003, included Stations 9-14 and was situated on the upper slope, with depths increasing from
93.6 m to 191.1 m. Three sediment grabs per station were collected using a Tri-Scoop 1000 rotating sampler affixed to a Phantom S2 remotely operated vehicle (ROV) (Figure 3). CTD casts using a Seabird SBE 911plus affixed with a Paroscientific digiquartz pressure transducer and a Biospherical QSP-200L light sensor were also taken to measure fluxes in temperature and irradiance (photosynthetically active radiation, or PAR) with depth at a scan rate of 24 Hz
(Figure 3). Sediment samples were analyzed immediately after collection using a light microscope to determine the presence or absence of live benthic diatoms, then bagged and refrigerated for further lab analysis on shore.
Depth measurements were taken using pressure transducers on the CTD and the ROV.
Though the CTD depth accuracy was 0.008%, because CTD casts were halted 10 m from the bottom to prevent damage to the rosette, ROV depths were more representative of sample collection depth, despite their 0.25 % accuracy. In addition, the
13
14
a.
Figure 2 a) Onslow Bay and Masonboro sample collection locations (Courtesy of Matthew Head, UNCW MS Marine Science, 2004).
14
142.6 m
122.5 m 67.7 m
15
93.2 m
162.8 m 1 km 1 km 127 m
b. c.
Figure 2. b) Transect 1 (Station 3 located at same site as Station 4). c) Transect 2.
15
16
a. b. c.
Figure 3. a) ROV Phantom S2. b) Tri-Scoop 1000 sediment scoop (circled). c) Seabird SBE 911plus CTD rosette.
16 pressure transducer on the ROV is located 1 foot (0.3048 m) above the bottom of the crash
frame, requiring this addition of depth to that shown on the display when the ROV reached bottom. However, because the ROV made a full descent to the bottom, these factors became less
important as the CTD depth would be compromised by the 10 m halting distance and ship
movement via wave motion at the sea surface. Therefore, any references to total depth from
surface to bottom will use depth recordings made by the ROV, while references to salinity,
temperature, and light, will use depth recordings made by the CTD.
-2 -1 Irradiance/PAR was measured in units of μE m- s . The percentage of surface incident
irradiance transmitted to the bottom was calculated by dividing the mean bottom irradiance by
the mean surface irradiance, and then multiplied by 100. Attenuation coefficients (kD), used as a
-kD proxy for water clarity, were calculated using the attenuation formula ID = IO e , where ID equals irradiance at the bottom of the water column, and IO equals irradiance at the surface.
Mean irradiance values for the surface and bottom were used for this formula. Raw kD values
were reported here; however, these values must be multiplied by 100 to obtain the percent
attenuation per meter of water, with lower values indicating higher water clarity.
Sample Preparation
Immediately following collection, wet strewn slides of bulk sediment were made and
examined on board the ship to determine the presence or absence of living diatoms. The
remaining bulk sediment was refrigerated in the dark and transported to the on shore lab for
immediate documentation of these live species, again using wet strewn slides. Individuals were
photographed using a Nikon Coolpix 995 digital camera affixed to an Olympus BH2 microscope
at 1250x magnification. Species were identified based on size, shape, and position of plastids
17 within the cell using a variety of texts including Hustedt (1930, 1955), Hendey (1964), John
(1983), and Round et al. (1990). A portion of each sample was processed using the following
methods to produce cleaned material suitable for species identification by light and scanning
electron microscopy: Five cc of each sample were placed in a 400 mL beaker filled with 50 mL
deionized water. Ten mL of 30 percent hydrogen peroxide (H2O2) and 0.1 g potassium
dichromate were added to remove any organics in the sample. After each sample was decanted
and rinsed three times with deionized water, excess deionized water was decanted until 50 mL of
the sample solution remained. Seven mL of 37% hydrochloric acid (HCl) was added to remove
any carbonates present. Following the reaction, each sample was again rinsed and decanted three
times, then diluted to 400 mL with deionized water. The final solution was thoroughly mixed,
then halved for light microscope and scanning electron microscope sample preparation.
Cover slip preparation for light microscope (LM) slides followed the settling technique used by Laws (1983). Three 22-mm cover slips were made for each sample and were mounted on slides using a naphrax/toluene solution and were progressively heated until evaporation of the toluene was complete. Excess naphrax was pressed out from under the mounted slip to remove bubbles and later scraped off.
To prepare scanning electron microscope mounts, a portion of each sample was vacuum- filtered through two Whatman 0.4-μm millipore discs and one Whatman 5-μm millipore disc.
After drying for 24 hours in a Thelco-130 drying oven at 75°F, the discs were cut into rectangular pieces and mounted on standard aluminum stubs. Three stubs were made using the
4-μm millipore cellulose nitrate membrane discs, and one stub was made using the 5-μm
millipore cellulose nitrate membrane disc. This combination of discs was used to ensure good
scanning electron microscope analysis. The 0.4 μm millipore disc was the preferred size as any
18 small diatoms would not be filtered through. In the event excess fine material obstructed frustule
visibility, 5-μm millipore discs served as a backup, eliminating the need to refilter the samples.
Once mounted, the stubs were sputter-coated with platinum palladium using a Cressington 208
HR sputter coater and Cressington MTM 20 thickness controller to a thickness of 6 nm. Samples
were then viewed using a Philips 1L XL-305 FEG scanning electron microscope.
Shallow-water samples were obtained by randomly selecting two archived intertidal
marsh samples from stations on Masonboro Island, North Carolina. These samples were
collected by a former graduate student, Heather Reesey, during the summer of 2000 as part of a
Cooperative Institute for the Coastal and Estuarine Environmental Technology (CICEET) program (Figure 4). Station samples included bulk sediment, previously cleaned material, and previously prepared light microscope slides. Cleaned material was processed a second time using the procedure mentioned above to ensure removal of carbonate and organic matter.
Microscope Analysis
All microscope analysis of each sample took place using one light microscope slide and one scanning electron stub. The remaining slides and stubs served as reserves in the event a particular slide or stub was damaged, or a stub displayed poor image resolution due to charging by the electron microscope. Taxonomic identification was done with both LM and SEM analysis using a ribbon-transecting method. Light microscope slides were analyzed at 1250x using ribbon transects traversing the entire area of the cover-slip. Photographs were taken at the magnification necessary to identify individual diatoms and document their morphologic features.
Twenty-one ribbon transects (seven at the top, middle, and bottom of the filter discs) on the SEM stubs were analyzed at 1250x. Again, photographs of individuals were taken at the
19
Figure 4. Masonboro Island, North Carolina sample locations (courtesy of R. Laws).
20
magnification necessary for taxonomic identification and documentation of morphologic
features.
In some cases, particularly for the genus Navicula, the chloroplasts of live diatoms
viewed in the light microscope obstructed the view of frustal ornamentation, making it difficult
to identify the diatom on the species level. In such instances, valves found in the SEM which
bore the same overall size and shape, and any similarities in ornamentation that might have been
visible in the LM specimen, were used.
Quantitative/Morphometric Analysis
Quantitative analysis took place by documenting, in cleaned material, the taxonomy and
frustal morphology of the species previously documented as live in the wet slides at the
shallowest and deepest of the 14 Onslow Bay stations, Stations 1 and 14. This ensured that only
species known to be alive at these areas were included in the study, as dead frustules could have
either settled from the photic zone or been carried in by currents from other areas. Omitting the
analysis of stations 2-13 was necessary due to limitations in time. Marsh samples from
Masonboro Island were analyzed using the same documentation methods; however, because all species present were considered native to the area (Hustedt 1955, Hilterman, 1998), differentiating between live and dead frustules was unnecessary. Using the light microscope, relative species abundances were established by counting 500 frustules of species previously
documented as live from Station 1 in Onslow Bay, 59 species from Station 14, and 500 frustules
each from both Masonboro Island stations. To delineate between unidentified species of both
areas, Roman numerals were assigned following the genus name for Onslow Bay species, and
21 capital letters were assigned following the genus name for Masonboro Island species (Appendix
E-G, K, M). If a particular unidentified species was present in both locations, a lower-case letter was assigned.
Using the scanning electron microscope stubs, 200 valves from each of the two
Masonboro Island sites, 200 valves of species previously documented as live from Stations 1, and 59 valves of species previously documented as live from Station 14 were measured and coded morphometrically using the following guide (Figure 5):
• Apical axis size o <10 µ o 10 μm ≤ n < 20 μm o 20 µ ≤ n < 30 µ o 30 µ ≤ n < 40 µ o > 40 µ • Symmetry o Radial Discoid shape • Intervalve distance less than valve diameter Cylindrical shape • Intervalve distance greater than valve diameter o Bilateral Raphe present • Monoraphid • Biraphid Raphe absent (araphid) Symmetry about axis • Ornamentation o Hyaline – Index 1 (<5% of valve surface covered by ornamentation) o Hyaline to complex – Index 2 (>5% but <50% valve surface covered by ornamentation) o Complex – Index 3 Stria-dominant (>50% valve surface striate with areolae) • Unoccluded areolae-dominant • Occluded areolae-dominant o Cribera o Rotae o Volae o Hymenes o Other Sterna-dominant (>50% valve surface covered with raised sterna)
22 b. c. d
e. f.
a.
g. h. i.
Figure 5. a) Division of diatom frustule into sectors. b) Radial discoid symmetry (scale = 10 μm). c) Radial cylindrical symmetry (scale = 10 μm). d) Bilateral symmetry, biraphid (scale = 5 μm). e) Bilateral symmetry, monoraphid (scale = 2 μm). f) Bilateral symmetry, araphid (scale = 5 μm). g) Hyaline ornamentation, Index 1 (scale = 2 μm). h) Hyaline to complex ornamentation, Index 2 (scale = 2 μm). i) Complex ornamentation, Index 3 (scale = 5 μm).
23 j. k. l.
m. n.
o. p.
Figure 5. j) Striae-dominant, unoccluded areolae (scale = 1 μm). k) Striae-dominant, occluded areolae, rotae (scale = 2 μm). l) Striae-dominant, occluded areolae, cribera (scale = 1 μm). m) Striae-dominant, occluded areolae, volae (scale = 2 μm). n) Striae-dominant, occluded areolae, hymenes (scale = 2 μm). o) Sterna-dominant (scale = 2 μm). p) Multiple ornamentation (scale = 2 μm).
24 Multiple ornamentation types (>50% of surface ornamented by a combination of aforementioned types)
Inequality of valves sampled between the deepwater and shallow water localities were due to the paucity of valves present in the sediments collected from Station 14, despite the higher
volume of sediment examined. Even after a full scan of 8 SEM stubs (4 to 8 times more than
was required for the other three samples), only 59 valves of species previously documented as
live from that station were found. Complete valves and fragments of valves were present in this
sample, but were also very scarce. Due to the 57.6 m difference in depth between Station 13 and
Station 14, valves from Station 13 could not be used to supplement the Station 14 sample size.
However, because the variety of habitats in the shallow water region is larger than the deepwater,
and a more diverse assemblage has been previously documented there by Hustedt (1955) and
Hilterman (1999), the diversity of taxa should be higher shallow water, thus alleviating any
biases introduced by differences in sample size.
Apical axes were measured from the valve margins, not including the thickness of the
girdle band. Ornamentation was assessed by printing scanning electron images of the
individuals, dividing the valve surface into a grid of eight sectors (for better qualitative
estimation of percent valve cover), and visually classifying it into an ornamentation type based
on the percentage of the valve surface covered by ornamentation. Because only three
ornamentation classes were used in this study and valve ornamentation was rarely irregular in
distribution on the valve itself, qualitatively assessing the percent valve cover by ornamentation
in this way was sufficient. An ornamentation index was established for quantification purposes
with an index of 1 applying to valves of the hyaline category, an index of 2 applying to valves of the hyaline to complex category, and an index of 3 applying to valves of the complex category.
Ornamentation terminology was used in accordance with Round, et al. (1990). Whenever
25 possible for the genus Cocconeis, quantification was done on the external side of dorsal valves, except in individuals in which the dorsal and ventral sides bore the same ornamentation. This method would ensure that the majority of valves measured were those valves most responsible for light collection. With the exception of a few genera, namely Amphora and Nitschia, which seem to have preferential settling orientations on both slides and vacuum filters, most individuals could be measured in this way. Finally, surface area to volume ratios of individuals were calculated from those live species at Stations 1 and 14 that were also present at the shallow-water
Stations DET I-B and ND IV-D. This was done by calculating the ratio of the surface area of the valve face to the total volume based on 20 individuals of each species from both the deepwater and shallow-water localities, collectively. Though these calculations assume a rectilinear shape, any biases will be continuous and proportional throughout the sample set. The results of these quantitative analyses were then correlated with the physical conditions of their respective areas recorded from CTD casts. CTD data logs for each station were imported into Microsoft Excel and SigmaPlot 9, with graphs made to better illustrate the fluxes in temperature and irradiance with depth for the duration of the cast’s descent. Basic conclusions regarding relation of species composition and frustal morphology to their respective environmental conditions were then made.
Following the individual station analyses from the deepwater and shallow water sites, comparisons were made between their respective stations to ascertain any differences in diatom species assemblage and morphometrics related to differences between their respective environments. Apical axis length, transapical axis length, ornamentation indices, and surface area to volume ratios from the collective morphometric analyses from each area were analyzed for variance using a one-way ANOVA to determine if differences in these parameters were
26 significant between shallow water and deepwater regimes. ANOVA was used due to the non- normal distribution of most of the morphometric data, even after log transformation. Differences between deepwater and shallow water datasets using ANOVA were accepted as significant when p-values were less than 0.05. Datasets returning p-values greater than 0.05 were considered non- significant, and were rejected.
Because any statistical analyses of the deepwater versus shallow water regions required that sample sizes between the two be equal, it was necessary to reduce the overall sample size of the shallow water valves from 400 to 259. To do this, data from 71 from Station DET I-B, and
70 valves from Station ND IV-D were randomly eliminated. This was done using a random number generator in SigmaPlot calibrated to select 71 and 70 non-repeating numbers ranging from 1 to 200. Since each valve measured was numbered consecutively, the random numbers generated by SigmaPlot were used as an extraction list. This caused slight fluctuations in mean apical and transapical axis lengths, and in the percent fractions of valves belonging to each morphometric category. These fluctuations were never more than 2%, however, and therefore deemed fit for further analyses.
27 RESULTS
Deepwater Locality: Onslow Bay
The 14 stations sampled in Onslow Bay were located within 60 nautical miles southeast
and east southeast of the mouth of the Cape Fear River, and ranged in water depths from 67.2 m
to 191.1 m (Figure 2, Appendix A). At shallower stations, ROV footage showed exposed marine
hard bottom outcrops, part of the Tertiary sequences of the Onslow Embayment on the Carolina
Platform (Riggs and Belknap, 1988). Bottom sediments began as poorly sorted, subangular
course sands, and grew finer with depth to very well sorted, rounded very fine to fine sands.
Irradiance/PAR values decreased exponentially with depth at all stations except Station 1, for which the decrease appeared more linear (Appendix B-D). This trend was likely the result of ship movement combined with surface layering due to the thermocline. Station 7 featured a sharp decrease in irradiance between 5 and 10 m depth, followed by an equally sharp increase to values greater than the values at the surface (Appendix C). This rebound in irradiance was followed by the expected exponential decrease in irradiance values with depth, indicating a period of time in which the CTD rosette likely passed under the ship’s shadow. Percent surface incident irradiation/PAR at the bottom decreased with station depth; however, attenuation coefficients fluctuated between 0.0443 (4.43% per meter) and 0.0842 (8.42% per meter), with water clarity being higher when coefficients are low (Figure 6-7, Appendix B). Surface water temperatures fluctuated very little while bottom water temperatures decreased with deeper station depths (Figure 8, Appendix B-D).
One hundred twenty-six species of diatoms were found in sediments collected in the deepwater stations (Appendix E). Of these, 122 species in 29 genera were identified at least to the genus level, with four valves unidentified at the genus level. Frustal orientation, poor
28 4 3.5 3 2.5 2 1.5 Percentage 1 0.5 0 Station 1 Station 2 Station 3 Station 6 Station 7 Station 8
a.
0.400
0.350 0.300 0.250
0.200 0.150
Percentage 0.100
0.050 0.000 Station 9 Station 10 Station 11 Station 12 Station 13 Station 14
b.
Figure 6. a) Transect 1 percent surface incident irradiation at the bottom of the water column. b) Transect 2 percent surface incident irradiation at the bottom of the water column.
29
0.090 0.080
0.070 0.060 s 0.050
0.040 kd Value kd 0.030
0.020 0.010
0.000 Station 1 Station 2 Station 3 Station 6 Station 7 Station 8
a.
0.070
0.060
0.050
s 0.040
0.030 Value kd 0.020
0.010
0.000 Station 9 Station 10 Station 11 Station 12 Station 13 Station 14
b.
Figure 7. a) Transect 1 attenuation coefficients (% attenuation per meter). b) Transect 2 attenuation coefficients (% attenuation per meter).
30
Transect 1 Surface and Bottom Water Temperatures
28
26
67.2 m 74.4 m 82.6 m
24 89.0 m
(°C) Temperature 22
Surface Temperature 102.4 m Bottom Temperature 121.0 m 20 Station 1 Station 2 Station 3 Station 6 Station 7 Station 8
a.
Transect 2 Surface and Bottom Water Temperatures
28
26
24
22 93.6 m 105.2 m
20 114.9 m 122.5 m
(°C) Temperature 133.5 m 18
16 Surface Temperature Bottom Temperature 191.1 m 14 Station 9 Station 10 Station 11 Station 12 Station 13 Station 14
b.
Figure 8. a) Transect 1 surface and bottom temperatures, with bottom depths. b) Transect 2 surface and bottom temperatures, with bottom depths.
31 preservation quality, and/or low species abundance contributed to the inability to identify some valves on the genus, and/or species level. Qualitative observations based on LM and SEM analysis estimated Cocconeis as the dominant genus for all 14 stations, closely followed by
Navicula, Amphora, Diploneis, Nitschia, and Achnanthes, based on relative abundances of these genera in bulk samples, strewn slides, and SEM stubs.
Transect 1
Stations 1-8 were sampled on October 16, 2003 and are located 51.7 nautical miles southeast of the Cape Fear River at the shelf-break region known as The Steeples, situated on the
Cape Fear Terrace (Figure 2). These stations made up a 2.12 nautical mile transect with depths ranging from 67.2 m at Station 1 to 121.0 m at Station 8 (Appendix A). Due to technical issues,
CTD casts were not made for Stations 4 and 5; however, two ROV dives took place at Station 3, with the second dive being labeled as Station 4. Percent surface incident irradiation/PAR at the bottom of the water column decreased from 3.740% at Station 1 to 0.0480% at Station 8 (Figure
6, Appendix B). Attenuation coefficients averaged 0.0640 (6.4% per meter) for all eight stations with the lowest value at Station 7 and the highest at Station 8 (Figure 7, Appendix B). Surface water temperatures increased slightly from 27.6 °C at Station 1 to 27.9 °C at Station 8 (Figure 8,
Appendix B). Bottom water temperatures decreased from 25.31 °C at Station 1 to 20.68 °C at
Station 8.
Microscopy of Transect 1 sediments yielded 123 species (Appendix E). Four species could not be identified to the genus level; however, the remaining 119 species represented 27 genera. At Station 1, fifty-five species of diatoms from 19 genera were recorded with one species unidentified to the genus level (Appendix F). Of these species, 9 species of the genera
32 Amphora, Cocconeis, Navicula, and Nitschia were found live in the sediments. Taxonomic
analysis on 500 valves of these living species showed that Cocconeis and Nitschia displayed the most species diversity with three species each (Table 1, Appendix G). However, the species
Cocconeis disculus was by far the most common diatom found, with 359, or 72% of the total number of valves. Morphometric analyses on 200 valves yielded a mean apical axis size of
14.31 μm and mean transapical axis size of 6.91 μm, with 110 valves, or 50%, falling in the 10
μm ≤ n < 20 μm category (Table 1, Appendix H). All valves were pennate in form (thus bilaterally symmetric) and since Cocconeis was the dominant genus, the most common valve type was monoraphid, which accounted for 177 valves, or 89%. The mean ornamentation index was 2.43, with 114 valves, or 57%, having hyaline to complex ornamentation. No valves had hyaline ornamentation. Unoccluded areolae was the dominant ornamentation type, with 133 valves, or 67%, though multiple ornamentation was also relatively common, with 42 valves, or
21%.
Transect 2
The upper-slope region of Onslow Bay was sampled on October 17, 2003, and lies approximately 37 nautical miles northeast of the Station 8 on the shelf break (60 nautical miles from the mouth of the Cape Fear River). Stations 9-10 made up the 5.26 nautical mile transect with depths ranging from 93.6 m at Station 9 to 191.1 m at Station 14
(Figure 2). Percent surface incident PAR at the bottom of the water column decreased from
0.356% at Station 9 to 0.028% at Station 14 (Figure 6, Appendix B). Mean attenuation coefficient values measured 0.0602 (6.02% per meter) and decreased with depth (Figure 7,
Appendix B). Surface water temperatures increased between Stations 9 and 14, from 27.65 °C to
33 Table 1. Station 1 taxonomic composition and morphometrics.
No. Species Counts Valves Amphora coffeaformis 24 Cocconeis disculus 359 Cocconeis distans 27 Cocconeis placentula 9 Navicula sp. a 15 Navicula digitoconvergens 17 Nitschia frustulum 6 Nitschia pellucida 7 Nitschia panduriformis 36
No. No. Apical Axis Size Valves Form Diversity Valves <10 μm 59 Pennate 200 10 μm ≤ n < 20 μm 110 Centric 0 20 μm ≤ n < 30 μm 16 No. 30μm ≤ n < 40 μm 13 Valve Type Valves >41 μm 2 Araphid 0 Monoraphid 177 No. Symmetry Type Valves Biraphid 23 Radial Discoid 0 No. Radial Cylindrical 0 Ornamentation Index Valves Radial Total 0 Hyaline - Index 1 0 Bilateral 200 Hyaline to complex - Index 2 114 Complex - Index 3 86 No. Dominant Ornamentation Type Valves Unoccluded areolae 133 Hymenate 7 Multiple 42 Volae 17 None 1
34 27.8 °C (Figure 8, Appendix B). Bottom water temperatures decreased between Station 9 and
14, from 22.9 °C to 14.9 °C.
Microscopy of sediments from Transect 2 excluded Stations 11-13 due to time restrictions and the paucity of valves present; however, because Station 14 was the deepest
location sampled, it was included. Stations 9-10 and 14 therefore yielded 29 species of diatoms
from 13 genera (Appendix E). Nine live species of diatoms from 6 genera were recorded from
sediments at Station 14. Of these, four species from the genera Actinoptychus, Amphora,
Cocconeis, and Nitschia were found live in the sediments (Table 2, Appendix I). A complete taxonomic and morphometric analysis could not be done for this station, once again, due to the paucity of valves present in the sediments. Though sands and silts could be separated from the bulk sample collected from this station, a high concentration of clays, particularly montmorillonite, remained. Due to similarities in size, shape, and density of montmorillonite and the majority of diatom frustules present, the processing and settling techniques used in this study were ineffective in concentrating the number of frustules required for the taxonomic and morphometric analyses. Despite attempting several variations of these techniques, only 59 total frustules were found (Table 2, Appendix J). Taxonomic analyses on this smaller subset yielded one species for each of the four genera, with Cocconeis disculus being the most numerous with
36 frustules, or 61% of the total.
Morphometric analyses showed that 45 frustules, or 76%, had apical axes less than 20
μm, with nearly equal numbers of frustules fitting into both the <10 μm and the 10 μm ≤ n < 20
μm categories. The mean apical axis length was 16.87 μm and mean transapical axis length was
8.96 μm. Fifty-seven frustules, or 97% were bilaterally symmetric, and 36 individuals, or 61%,
35 Table 2. Station 14 taxonomic composition and morphometrics.
No. Species Counts Valves Actinoptychus splendens 2 Cocconeis disculus 36 Diploneis chersonensis 3 Nitschia panduriformis 18
No. No. Apical Axis Size Valves Form Diversity Valves <10 μm 24 Pennate 57 10 μm ≤ n < 20 μm 21 Centric 2 20 μm ≤ n < 30 μm 7 No. 30μm ≤ n < 40 μm 3 Valve Type Valves >40 μm 4 Araphid 2 Monoraphid 36 No. Symmetry Type Valves Biraphid 21 Radial Discoid 2 No. Radial Cylindrical 0 Ornamentation Index Valves Radial Total 2 Hyaline - Index 1 0 Bilateral 57 Hyaline to complex - Index 2 36 Complex - Index 3 23 Dominant Ornamentation No. Type Valves Unoccluded areolae 50 Volae 9
36 were monoraphid (accounting for the higher volume of Cocconeis disculus in the sample).
Biraphid frustules were also relatively common, due to the frequency of Nitschia panduriformis.
Unoccluded areolae was the most common dominant ornamentation type, with 50 individuals, or
85%. The ornamentation index averaged 2.43, with hyaline to complex ornamentation (Index 2)
accounting for 36 frustules, or 61%; however, complex ornamentation (Index 3) was also
relatively common, with 23 frustules, or 39%.
Surface area to volume ratios were performed on valves of the species previously
documented as live, Cocconeis disculus, Fallacia forcipata, Navicula sp. a, Nitschia frustulum,
and Nitschia panduriformis, which were also present in the shallow water sediments (Table 3,
Appendix O). The lowest ratios belonged to Navicula panduriformis, averaging 0.216, while
Cocconeis disculus had the highest mean ratio with 0.592.
Shallow water Locality: Masonboro Island
Masonboro Island is an undeveloped 13.3 km long barrier island south of Wrightsville
Beach, North Carolina. The island width ranges from 60 m to 1.6 km with a narrow beach on the ocean side and dune ridges extending into a large back-barrier Spartina alterniflora marsh on the
sound side. The island is a semi-diurnal microtidal system with a mean amplitude of 1.15 m
(Panasik, 2003). Marsh deterioration has been problematic on Masonboro Island, resulting in net
sediment loss from erosion. Renourishment of both deteriorated and non-deteriorated areas of
the island has taken place to mitigate this issue and has consequently changed the sediment
composition for these areas. Fractionation estimates prior to renourishment were 50% fine silts and 50% fine grained sands for both deteriorated and non-deteriorated sites (Panasik, 2003).
37 Table 3. Deepwater mean surface area to volume ratios by species.
Species Mean S/V Ratio Cocconeis disculus 0.592 Fallacia forcipata 0.225 Navicula sp. a 0.446 Nitschia frustulum 0.523 Nitschia panduriformis 0.216
38 Mean grain size rose from 0.10-0.11 mm before renourishment to 0.244-0.321 mm after, with the mean grain size of the dredge spoil fill being 0.56 mm (Panasik, 2003; Croft, 2003).
Samples from Masonboro Island were taken from intertidal sediments in both deteriorated and non-deteriorated sites that were previously renourished by dredge spoils (Figure
4). Non-deteriorated sediment samples were given the prefix “ND” in their station number, while deteriorated sediment samples were given the prefix “DET”.
Station DET I-B
Of the 500 valves counted, 107 species of 25 genera were found, with 7 species unidentified to the genus level (Table 4, Appendix K). The genera Navicula, Nitschia, and
Amphora exhibited the highest species diversity with 26, 19, and 13 each, respectively, and accounted for the most number of valves with 138, 62, and 66 each, respectively.
Of the 200 valves quantified using morphometric analyses, 181 (91%) were pennate in form, and 19 (9%) were centric in form (Table 4, Appendix L). Most valves had bilateral symmetry, accounting for 181 valves (91%). Nineteen valves were radially symmetric with 15 valves being radial cylindrical (80%, or 7.5% of the total) and 4 valves being radial discoid
(20%, or 2% of the total). Biraphid diatoms made up the majority of valve types with 132 valves
(66%). Araphid and monoraphid types included 60 valves (30%) and 8 valves (4%), respectively. Apical axis measurements averaged 25.79 μm, while transapical axis measurements averaged 7.87 μm, with most valves being under 20 μm. Complex ornamentation
(Index 3) and hyaline to complex ornamentation (Index 2) dominated the valve ornamentation types with 101 valves (50.5%) and 98 valves (49%), respectively. Unoccluded areolae and multiple ornamentation types were the most common among dominant ornamentation with 98
39 Table 4. Station DET I-B taxonomic composition and morphometrics.
No. No. Individuals Per Genus Valves Apical Axis Size Valves Achnanthes 17 <10 μm 46 Amphora 66 10 μm ≤ n < 20 μm 76 Bacillaria 5 20 μm ≤ n < 30 μm 37 Biddulphia 3 30μm ≤ n < 40 μm 16 Campylosira 1 >40 μm 25 Cerataulus 1 No. Cocconeis 32 Symmetry Type Valves Cyclotella 2 Radial Discoid 4 Delphenies 27 Radial Cylindrical 15 Dimeregramma 21 Radial Total 19 Diploneis 8 Bilateral 181 Entomoneis 4 No. Eunotogramma 2 Form Diversity Valves Fallacia 15 Pennate 181 Fragilaria 16 Centric 19 Gyrosigma 9 No. Melosira 8 Valve Type Valves Navicula 138 Araphid 60 Nitschia 62 Monoraphid 8 Odontella 2 Biraphid 132 Opephora 28 No. Paralia 6 Dominant Ornamentation Type Valves Plagiogramma 1 Unoccluded areolae 98 Rhopalodia 2 Hymenate 26 Thalassiosira 15 Rotae 15 Unknown 9 Cribera 7 Multiple 52 None 2
No. Ornamentation Index Valves Hyaline - Index 1 1 Hyaline to complex - Index 2 98 Complex - Index 3 101
40 valves (49%) and 52 valves (26%), respectively. The ornamentation index for this station
averaged 2.5.
Station ND IV-D
Ninety species of 26 genera of diatoms comprised the total 500 valves counted (Table 5,
Appendix M). Navicula and Nitschia accounted for the most number of individuals per species, with 143 individuals (29%) and 79 individuals (16%), respectively, and were the most diverse in terms of species per genera, with 25 species and 14 species, respectively. Various species of
Amphora, Cocconeis, and Melosira, were also relatively common with between 30 and 37 individuals each, though Amphora and Cocconeis were more diverse in terms of species per genus.
Of the 200 valves sampled for morphometric analyses, 164 valves (82%) were pennate in form and bilaterally symmetric, and 36 (18%) were centric. Most centric forms were radial- cylindrical in symmetry, accounting for 35 valves (97%, or 18% of the total). One hundred thirty-two valves were biraphid (66%), 57 valves were araphid (29%), and 11 valves were monoraphid (5%). The mean apical and transapical axis sizes were 22.81μm and 7.36 μm, respectively. Over half the valves sampled had apical axes less than 21 μm, accounting for 132 total valves (66%), though the dominant apical axis size range was between 10 μm and 20 μm, with 83 valves (42%). Like Station DET I-B, unoccluded areolae was the most common dominant ornamentation type with 116 valves (58%) though the multiple ornamentation type was also common, accounting for 53 valves (26.5%). All valves were either hyaline to complex
(Index 2) or complex (Index 3) in ornamentation, with 105 (52.5%) and 95 (47.5%) respectively.
The ornamentation index for this station averaged 2.48.
41 Table 5. Station ND IV-D taxonomic composition and morphometrics.
No. Individuals Per Genus Valves Apical Axis Size No. Valves Achnanthes 3 <10 μm 49 Actinoptychus 2 10 μm ≤ n < 20 μm 83 Amphora 30 20 μm ≤ n < 30 μm 30 Bacillaria 4 30μm ≤ n < 40 μm 13 Campylosira 1 >40 μm 25 Cocconeis 34 Coscinodiscus 2 Symmetry Type No. Valves Cyclotella 12 Radial Discoid 1 Cymatosira 2 Radial Cylindrical 35 Delphenies 23 Radial Total 36 Dimeregramma 14 Bilateral 164 Diploneis 8 Entomoneis 2 Form Diversity No. Valves Eunotogramma 7 Pennate 164 Fallacia 12 Centric 36 Gyrosigma 11 Melosira 37 Valve Type No. Valves Navicula 143 Araphid 57 Nitschia 79 Monoraphid 11 Odontella 1 Biraphid 132 Opephora 25 Paralia 18 Dominant Ornamentation Type No. Valves Plagiogramma 2 Unoccluded areolae 116 Pleurosigma 2 Hymenate 12 Rhopalodia 1 Rotae 15 Thalassiosira 25 Cribera 3 Multiple 53 Volae 1 None 0
Ornamentation Index No. Valves Hyaline - Index 1 0 Hyaline to complex - Index 2 105 Complex - Index 3 95
42 Mean surface area to volume ratios showed that Nitschia frustulum had the highest mean
ratio at 0.648, while Fallacia forcipata had the lowest mean ratio at 0.237 (Table 6, Appendix
O).
Deepwater/Shallow water Comparison
Though more valves of benthic diatoms were measured in the shallow water stations than
the deepwater stations, two important factors must be noted. First, the volume of deepwater
sediment examined greatly exceeds the volume of inshore sediment examined due to the greater
number of deepwater stations. Were equal volumes of sediment examined for both regions, it
would be expected that the number of taxa and individuals would be higher in the shallow water
regions. Second, frustules of species found alive in the deepwater samples were used in the
morphometric analyses, and were both less abundant and less diverse in the deepwater region
compared to the shallow water region based on microscopy of wet mount slides from deepwater.
Though diatoms present in the Masonboro Island samples were dead at the time of this study, it
is presumed the taxonomic composition of those samples represents a subset of the live
assemblage in that area based on a comparison with previous studies and the wider variety of
habitats and substrates on which these species can live (sands, muds, rocks, plants, etc.) versus the deepwater (Hustedt, 1955; Hilterman, 1999). In the end, despite differences in sample sizes, fluctuations less than 2% occurred in the percentages of valves in each morphometric category when 141 valve measurements were extracted from the total sample size of 400 (Table 7).
The mean apical axis length for deepwater valves measured 14.89 μm, while the same for
shallow water valves was 51% larger, at 22.54 μm (Table 8). P-values returned in the one-way
ANOVA for this parameter equaled 8.6 x 10-6, indicating a significant increase in apical axes
43 Table 6. Shallow water mean surface area to volume ratios by species.
Species Mean S/V Ratio Cocconeis disculus 0.578 Fallacia forcipata 0.237 Navicula sp. a 0.411 Nitschia frustulum 0.648 Nitschia panduriformis 0.454
44
Table 7. Morphometric analysis of 400 shallow water valves versus morphometric analysis of a subset of 259 randomly selected valves from the same sample.
(n = 400) (n = 259) Mean Apical Axis Length 23.80 μ 22.54 μ Mean Transapical Axis Length 7.61 7.43 μ
Mean Ornamentation Index 2.49 2.48
Morphology Percentage Percentage Pennate 86.25% 87% Centric 13.75% 13% Bilateral 86.25% 87% Radial discoid 1.25% 1% Radial cylindrical 12.50% 12% Biraphid 66% 65.25% Monoraphid 4.75% 5.5% Araphid 29.25% 29.25% Index 1 0.25% 0% Index 2 50.75% 52.75% Index 3 49% 47.25% Unoccluded areolae 53.50% 54% Hymenate 9.50% 9.25% Volae 0.25% 0.375% Cribera 2.50% 2.75% Rotae 7.50% 7% Multiple 26.25% 26.25% None 0.50% 0.375%
45 Table 8. Deepwater/shallow water morphometric comparison using same sample sizes (n = 259).
Shallow water Deepwater Valves Valves Mean Apical Axis Length 14.89 μm 22.54 μm Mean Transapical Axis Length 7.37 μm 7.43 μm Mean Ornamentation Index 2.42 2.44
Deepwater (n = 259) Shallow water (n = 259) Number of Morphological Parameter Valves Percentage Number of Valves Percentage Pennate 257 99% 225 87% Centric 2 1% 34 13% Bilateral 257 99% 225 87% Radial discoid 0 0% 3 1% Radial cylindrical 2 1% 31 12% Biraphid 44 17% 169 65.25% Monoraphid 213 82% 14 5.5% Araphid 2 0.75% 76 29.25% Index 1 0 0% 0 0% Index 2 150 58% 134 52.75% Index 3 109 42% 125 47.25% Unoccluded areolae 183 70.75% 140 54% Hymenate 7 2.75% 24 9.25% Volae 26 10% 1 0.375% Cribera 0 0% 7 2.75% Rotae 0 0% 18 7% Multiple 42 16% 68 26.25% None 1 0.50% 1 0.375%
Deepwater S/V Shallow water Species Ratio S/V Ratio Cocconeis disculus 0.592 0.578 Fallacia forcipata 0.225 0.237 Navicula sp. a 0.446 0.411 Nitschia frustulum 0.523 0.648 Nitschia panduriformis 0.216 0.454
46 lengths in shallow water valves (Table 9). Mean transapical axis length for deepwater valves was 7.37 μm, non-significantly smaller than shallow water valves which averaged 7.43 μm. The
mean ornamentation index also varied very little and was considered non-significant between the
two localities. The ornamentation index for deepwater valves averaged 2.42, while shallow
water valves were 0.83% larger, at 2.44. Hyaline to complex ornamentation was most common
in both regimes, accounting for just over half the total valves sampled, though all of the
remaining valves had complex ornamentation. In both localities, unoccluded areolae was the
most common dominant ornamentation type; however, was 16.75% more common in the
deepwater valves than those in the shallow water. Multiple ornamentation types were also
common, though were 10.25% more prevalent in the deepwater valves than the shallow water.
Ninety-nine percent of valves sampled in the deepwater stations were both pennate in
form and bilaterally symmetrical, as expected in a deepwater benthic assemblage. In contrast,
87% of valves were both pennate and bilateral in shallow water samples, accounting for a few
centric forms that can be present in benthic assemblages under shallow-water conditions. Most
of these centric forms were radial cylindrical in symmetry, and upon species analysis, are
typically chain-forming colonial species that adhere to substrates or are planktonic. Deepwater
valves were dominated by monoraphid valve types, due to the vast abundance of Cocconeis
species in the assemblage. Though monoraphids forms were present in the shallow water
morphometric analysis, they accounted for only 5.5% of the total number of valves examined.
The biraphid valve type was much more prevalent, accounting for 65.25% of the shallow water
total, and is due to the prevalence of Navicula, Nitschia, and Amphora in the taxonomic
assemblage. Araphid valves were also relatively numerous in the shallow water analysis,
47 Table 9. ANOVA results for deepwater versus shallow water morphological and S/V ratio parameters.
Morphological: Parameter F-value df P-value Apical Axis 20.2 1, 516 0.0000086 Transapical Axis 2.73 1, 516 0.099 Ornamentation Index 0.193 1, 516 0.66
S/V Ratio: Species F-value df P-value Cocconeis disculus 0.0578 1, 38 0.81 Fallacia forcipata 9.17 1, 38 0.0044 Navicula sp. a 14.75 1, 38 0.00045 Nitschia frustulum 7.64 1, 38 0.0088 Nitschia panduriformis 14.46 1, 38 0.00050
48 accounting for 29.25% of the total valves, and all but absent in the deepwater with 0.75% of the
total valves.
Significant differences in mean surface area to volume ratios occurred in all species
sampled between deepwater and shallow water locations, with the exception of Cocconeis
disculus (Table 9). Fallacia forcipata, Nitschia frustulum, and Nitschia panduriformis were significantly lower in their S/V ratios in deepwater stations, while Navicula sp. a had a significantly larger S/V ratio in the deepwater stations. This shows that for three species, the frustule took on a more cylindrical shape, while one took on a discoid shape in deepwater. S/V ratios for Cocconeis disculus were not significantly different between the deep and shallow water regimes.
In summary, the following overall findings were drawn based on the abovementioned results: 1) benthic marine diatoms were located at depths substantially deeper than the previously recorded maximum depth by Plant-Cuny (1978); 2) these diatoms were present in areas where the percent surface incident irradiation flux to the bottom was as low as 0.028%, far lower than the traditionally accepted 1% compensation depth; 3) both the taxonomic diversity and diversity of forms of benthic diatoms were greater in the shallow water region; 4) apical axis lengths were significantly higher in the shallow water region, but no significant difference in transapical axis length and ornamentation existed; and 5) surface area to volume ratios were significantly lower in the deepwater region for three of the five species measured, indicating that frustules may be more cylindrical-shaped than discoid.
49 DISCUSSION
Benthic diatoms are not typically believed to be found in deepwater areas due to
limitations in light availability. Nevertheless, assemblages have been found in situ in these areas
and are probably not transients swept from the shore by wave energy and ocean currents. The
higher fucoxanthin:chlorophyll a ratios documented at depths up to 63 m in Onslow Bay indicate
an adaptation to low light conditions, as such high ratios in shallow water floras do not exist
(Cahoon et al. 1992). Should shallow water floras be swept into deeper water via physical
processes, the high fucoxanthin:chlorophyll a ratio signal would be dampened. Though
fucoxanthin:chlorophyll a ratios were not examined from the fourteen Onslow Bay station
samples collected in this study, evidence still suggests the species from these samples are likely
in-situ residents and not transported from the 63 m depth area. Physical forcing by waves and strong currents do not generally penetrate to the depths sampled in this study, except perhaps during storm events. No such event took place prior to the sampling cruise, and though a mild current affected ROV operations, the velocity was not sufficient to move the predominantly sandy sediments, as witnessed by the absence of turbidity and sediment movement on the bottom in the live ROV footage. Furthermore, the vast majority of the live benthic species noted were epipsammic. No tychopelagic species were found, and the one planktonic species documented,
Actinoptychus splendens, is a larger and more robust species than most planktonic species, which would account for its presence, albeit rare, in these sediments. Finally, if benthic diatoms are transported from the locations sampled by Cahoon et al. (1992), it would be expected that their presence in deeper sediments would be patchy, being dependent on the direction and strength of the current. Nevertheless, they were documented in this study continuously at all fourteen stations.
50 Taxonomic diversity and composition are the more obvious differences that exist
between deepwater benthic diatoms of Onslow Bay, North Carolina and those living in the
adjacent shallow water regions. The variation in environmental conditions between these
regions is undoubtedly the reason for this difference, with light availability likely being the most
important factor. With this in mind, does the exterior morphology of the benthic diatoms in these areas reflect adaptations to their respective shallow water or deepwater location, or does
the adaptation exist in their physiology? Is it in both?
Potential habitats for benthic diatoms are much more diverse in marsh and estuarine
environments compared to environments in the deepwater. In shallower and/or less turbid waters
where ample irradiance reaches the bottom, planktonic diatoms typically found in the water
column may occasionally settle to the bottom, live for a time, and become resuspended
(tychopelagic) without disrupting their metabolic processes. Likewise, colonial chain-forming
diatoms may adhere to benthic substrates, and any mobile benthic species may migrate through
the upper few millimeters of the sediment based on irradiance flux. In deepwater environments
however, the variety of habitats becomes much lower. On the deepwater sand flats in Onslow
Bay, epiphytic diatom habitats are absent, and depending on the distance from shore,
epipsammic diatom habitats give way to epipelic habitats. Few live tychopelagic or benthic
colonial chain-forming species would be found in the benthic environments. Epilithic diatoms
may be found on exposed marine hard bottom reefs, however would likely be less numerous than
epipsammic and epipelic diatoms, as sand/mud environments are relatively more common.
It should therefore not be surprising that species diversity and diversity of morphological
features is lower in the deepwater stations sampled in this study. Biases in the sample sizes used
in this study are no doubt of concern; however, thorough qualitative inspection of samples took
51 place prior to taxonomic and morphometric analyses, and little variation in the results would
likely have taken place had the sample size for Station 14 in the deepwater regime been greater.
Light and scanning electron microscopy yielded very few valves in general, and very few valves
of the live species, in particular. The abundance of montmorillonite in Station 14 sediments
made concentrating the number of valves all but impossible. Because the clay size fraction,
shape, and density of montmorillonite was nearly identical to that of the diatoms, heavy liquids,
settling, and decantation techniques were ineffective. Because centrifugation is simply a form of
settling, it was ruled out as a possible separation method. Biomarkers and labeling may be a
valid option in future studies, however.
External Morphology
The presence of living diatoms in dark regions is not a newly discovered phenomenon,
though it was commonly accepted that they, like some other phytoplankton species, may become inactive by entering into a resting spore stage. Alternatively, Jochem (1999) noted that the
diatoms in his phytoplankton assemblage remained in the active state when he exposed them to long periods of darkness, and in fact, began to reproduce immediately upon their return to normal light conditions. These observations were also made by Murphy and Cowles (1997).
Though some diatoms have been noted to revert to heterotrophy in low-light conditions, this ability is not likely to be a useful advantage due to the high metabolic cost of producing and maintaining both autotrophic and heterotrophic processes (Peters, 1996; Peters & Thomas,
1996). Less costly adaptations such as increased size or surface area to volume ratios may be an
alternative, though only one relevant study, done by Nayer et al. (2005), has been found that
52 explores these parameters. The data presented here do not readily fit with the data of Nayer et
al., though the varying methods by which cells were measured may account for this discrepancy.
No studies comparing valve ornamentation and its effects on light collection in diatoms
have been published, but no significant difference has been noted in ornamentation indices
between the deep and shallow-water floras in this study. The surface area to volume ratios, however, do show some significant differences, at least at the genus level, between the shallow water and deepwater regimes. Rather than frustules growing more discoid in shape with depth, three of the five species used in the S/V ratio analysis were more cylindrical. The two species of
Nitschia and Fallacia forcipata in this study showed significant decreases in S/V ratios in deepwater, indicating that the surface area of the valve face was proportionately smaller in that region. Navicula sp. a showed a significantly larger S/V ratio in the deepwater, illustrating that its valve face was proportionately larger in the deepwater. Cocconeis disculus showed no significant difference in S/V ratios between deep and shallow water. It appears, for at least some species, an allometric decrease takes place in valve size, with apical and transapical axes becoming smaller with depth relative to the pervalvar axis. This is reflected by the greater fluctuation in maximum and minimum apical and transapical axes lengths as compared to the same fluctuations in pervalvar axis lengths (Appendix O). Navicula sp. a does not fall into this category, nor does Cocconeis disculus, suggesting that changes in S/V ratio may be linked to taxonomy rather than the assemblage as a whole. The tendency of Cocconeis disculus to retain its discoid shape despite depth, coupled with its high percentage in the deepwater stations might suggest that the discoid shape is more advantageous. However, this does not account for the turnover in shape from discoid to cylindrical in three of the remaining four species. A more thorough examination of S/V ratio using larger sample sizes and/or a wider variety of species
53 common to both the deep and shallow water regimes could help flush out whether or not these differences are indeed taxonomic responses. If taxonomy does seem to play a role, more in- depth studies of the characteristics of these species and their responses under varying conditions should follow.
Physiology
Chloroplast size and pigment content are more common parameters of study for assessing phytoplankton growth and production, and much research has been done to assess their relation with external factors, including nutrient and light availability and fluctuations in temperature, salinity, and oxygen. The metabolic cost of variation in pigmentation of phytoplankton is also much lower compared to the ability to convert to heterotrophy, and high fucoxanthin:chlorophyll a ratios are commonly associated with light-limited diatoms. This phenomenon has been noted in sediments in the 60 m depth range in Onslow Bay, North Carolina (and extrapolated to depths of 90 m), with ratios being two to over seven times higher than in sediments from shelf sites in
Onslow Bay, as well as regions in Stellwagen Bank off the Massachusetts coast and the Florida
Keys (Cahoon et al., 1992; Cahoon and Laws, 1993). Mouget et al. (2004) took this one step further by finding increased fucoxanthin concentrations and higher fucoxanthin:chlorophyll a ratios in the cultures of the marine diatom Haslea ostrearia when incubated with blue and green light under low-light conditions, compared to a white light control at the same intensity as well yellow, red, and far-red light variables.
Other factors may be at work, however, as discussed by Goericke et al. (2000) in their research on the picoplankton Prochlorococcus. Though strains of Prochlorococcus were thriving at depths of 80 m to 140 m in the Arabian Sea and the tropical Pacific off Mexico, the
54 irradiance levels at these depths was low enough to, at best, greatly retard growth despite abnormally high pigment concentrations present in the genus. Rather than finding higher fucoxanthin:chlorophyll a ratios, high concentrations of an unusual carotenoid complement,
7’,8’-dihydro-derivative of zeaxanthin (believed to be the carotenoid parasiloxanthin) were discovered. This was hypothesized to be the key adaptation based on its high concentrations in
Prochlorococcus grown in low-light, low-temperature cultures.
Chloroplast size and the presence or absence of certain pigments and their concentrations was not a parameter tested in this study Nevertheless, it has been demonstrated that it is certainly an interesting avenue of future research in Onslow Bay in light of the results indicating that only shape differences seem to occur between the deep and shallow-water regimes of this area. Some research has already been done by Cahoon et al. (1992) and Panasik (2003) contrasting the concentrations of chlorophyll a between Onslow Bay and Masonboro Island, with deepwater (>100 m) concentrations ranging from over 20 mg m-2 to less than 5 mg m-2.
Fucoxanthin:chlorophyll a ratios were not reported for Masonboro Island; however, based on comparisons by Cahoon et al. (1992), it is expected that ratios would be lower compared to deepwater sites.
Implications
That benthic diatoms can live and photosynthesize in deepwater conditions has interesting biological implications, particularly in terms of nutrient fluctuation. Not only does this add a new variable for which biologists may need to account when estimating rates of, and methods of, nutrient cycling, but also any associated feedback loops could have the potential to greatly affect the food web. Cahoon (1999) establishes this idea and states that as gate-keepers
55 of the sediment/water interface, benthic diatoms are highly likely to impact biochemical movement through the area. Furthermore, Yin et al. (1998) were able to demonstrate a reduction in nitrate uptake inhibition by ammonium in diatoms living in low light conditions. Though
Onslow Bay is considered an oligotrophic regime as a whole, phosphorous is abundant due to
Neogene phosphorus deposits on the Carolina Platform (Riggs, 1983), and upwelling occurs at the shelf-break region. It is therefore presumed that the only limiting factor for deepwater benthic diatom communities for this area would be light.
The presence of benthic diatoms provides a food source for grazers; therefore diatoms in deepwater regimes may extend the range of grazers typically found in shallower waters, and/or may provide a new source of food for deepwater grazers (Cahoon, 1999). If present in abundance, benthic diatoms therefore may exert a significant impact on local food web dynamics. Because they are actively photosynthesizing and reproducing, their nutritional value is higher as compared to diatoms living in resting spore stages, and would serve as a more valuable food source.
Continental margin environments are dynamic areas where coastal processes meet those of the open ocean. Nutrient levels are typically higher on average due to export from near-shore environments via river and tidal inputs, though seasonal upwelling from the slope may also occur and add nutrients, as well as oxygen, from the deep sea. Combined effects of nutrient levels, and warmer water temperatures associated with the shallower depths, causes most margin environments, as a whole, to be more productive than the adjacent open ocean. Primary productivity in these regions, however, is commonly thought to be limited to the water column, with compensation depths varying based on light availability and mixing dynamics. In addition, in areas with wide continental margins, rates of primary productivity may decrease with distance
56 from the shore as nutrient resources become diffuse and/or depleted. If the results of this study
hold for the entire continental margin in this area, estimates of the rate of primary productivity
here, and thusly productivity as a whole, have been greatly underestimated. Furthermore, the
estimated rates of primary productivity for all continental margins, at least within temperate zones, may be underestimated as well. At the very least, the factors affecting primary productivity in these margin environments have been misunderstood.
57 CONCLUSIONS
This study supports previous work that has established that benthic microalgae can adapt
and survive under conditions traditionally believed to not support photosynthetic growth.
Though not as abundant or taxonomically diverse in the deepwater regions, benthic diatoms are
actively living and photosynthesizing at depths up to 191 m with surface incident PAR fluxes as
low as 0.028%, significantly below the 1% compensation depth. While Nayer et al. (2005) has
shown that external morphology may play a role in adapting to such conditions, this study
demonstrates that as a whole, surface area to volume ratios exhibited the only major difference.
The frustules of the deepwater assemblage, when taken as a whole, were largely discoid in shape,
characterized by higher S/V ratios reflected in the abundance of Cocconeis disculus. However,
when examined taxonomically, S/V ratios fluctuated between the deep and shallow water
frustules. Because only apical axes were significantly different between the deep and shallow
water assemblages, frustules may be shrinking allometrically with depth. This conclusion does not completely refute the hypothesis that external morphological features are the distinguishing
characteristics of benthic diatoms for these two regimes, but certainly size and ornamentation do
not appear to be as important as shape. Chloroplast size, pigment concentrations, and pigment
ratios are also likely factors based on their documented variations elsewhere; however, other
unknown variables may also be at work. More research, such as HPLC analyses, can help to
determine some of these variables.
Regardless of their adaptation, the presence of active benthic diatoms in Onslow Bay has
the potential to impact nutrient cycling and the food web of the region. Light availability is
likely the only factor limiting their abundance; however, they may still provide valuable food
sources for local grazers and/or extend the ranges of grazers from surrounding areas. A more
58 widespread assessment of benthic diatom communities, including higher resolution studies of
their abundance with depth, impacts on nutrient cycling at the sediment/water interface, and nutrient limitation should be done to estimate their influence in this region.
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64 APPENDIX
Appendix A. Deep water station sample dates, coordinates, and depths.
Station Date Coordinates Depth (m) 1 10/16/2003 33'12.0 N 77'22.0 W 67.2 2 10/16/2003 33'11.700 N 77'23.107 W 74.4 3 10/16/2003 33'11.456 N 77'23.540 W 82.6 4 10/16/2003 33'11.456 N 77'23.540 W 82.6 5 10/16/2003 33'11.11 N 77'25.113 W 91.7 6 10/16/2003 33'11.13 N 77'25.25 W 89.0 7 10/16/2003 33'10.91 N 77'24.66 W 102.4 8 10/16/2003 33'10.562 N 77'23.846 W 121.0 9 10/17/2003 33'36.223 N 76'51.823 W 93.6 10 10/17/2003 33'35.794 N 76'51.681 W 105.2 11 10/17/2003 33'35.421 N 76'51.335 W 114.9 12 10/17/2003 33'34.817 N 76'51.167 W 122.5 13 10/17/2003 33'34.087 N 76'50.989 W 133.5 14 10/17/2003 33'32.56 N 76'47.405 W 191.1
Appendix B. Deep water irradiance/PAR flux to the bottom of the water column, attenuation coefficients, surface temperature and bottom temperature, by station.
Mean Mean Surface Bottom PAR Flux (%) kD (% m-2) Temp (°C) Temp (°C) Station 1 3.740 0.0497 27.599 25.316 Station 2 0.830 0.0721 27.594 25.291 Station 3 0.776 0.0674 27.64 25.352 Station 6 0.355 0.0661 27.744 24.266 Station 7 1.089 0.0443 27.806 21.407 Station 8 0.048 0.0842 27.897 20.682 Station 9 0.356 0.0647 27.648 22.887 Station 10 0.320 0.0658 27.649 22.893 Station 11 0.079 0.0666 27.901 20.767 Station 12 0.119 0.0581 27.919 20.295 Station 13 0.031 0.0616 27.831 19.634 Station 14 0.028 0.0446 27.759 14.931
Appendix C. Deep water irradiance/PAR profiles by station.
Station 1
Irradiance/PAR (uE m-2 s-1)
0 50 100 150 200 250 0
10
20
30
40 Depth (m)
50
60 Irradiance Temperature 70 25.0 25.5 26.0 26.5 27.0 27.5 28.0 Temperature (°C)
Station 2
Irradiance/PAR (uE m-2 s-1)
0 200 400 600 800 1000 1200 1400 1600 0
10
20
30
40 Depth (m)
50
60 Irradiance Temperature 70 25.0 25.5 26.0 26.5 27.0 27.5 28.0 Temperature (°C)
66
Station 3
Irradiance/PAR (uE m-2 s-1)
0 250 500 750 1000 1250 1500 1750 2000 0
10
20
30
40 Depth (m) 50
60
Irradiance 70 Temperature
25.0 25.5 26.0 26.5 27.0 27.5 28.0
Temperature (°C)
Station 6
Irradiance/PAR (uE m-2 s-1)
0 500 1000 1500 2000 2500 3000 0
10 20
30
40
50 Depth (m) 60
70
80 Irradiance Temperature 90 24.0 24.5 25.0 25.5 26.0 26.5 27.0 27.5 28.0 Temperature (°C)
67
Station 7
Irradiance/PAR (uE m-2 s-1)
0 25 50 75 100 125 150 175 200 0
20
40
60 Depth (m) 80
Irradiance 100 Temperature
21 22 23 24 25 26 27 28 29 Temperature (°C)
Station 8
Irradiance/PAR (uE m-2 s-1)
0 250 500 750 1000 1250 1500 1750 2000 0
20
40
60 Depth (m)
80
100 Irradiance Temperature 120 20 21 22 23 24 25 26 27 28 29 Temperature (°C)
68
Station 9
-2 -1 Irradiance/PAR (uE m s )
0 200 400 600 800 1000 0
20
40
Depth (m) 60
80 Irradiance Temperature
22 23 24 25 26 27 28
Temperature (°C)
Station 10
Irradiance/PAR (uE m-2 s-1)
0 150 300 450 600 750 900 0 10
20
30
40
50 Depth (m)
60
70 80 Irradiance Temperature 90 22.5 23.0 23.5 24.0 24.5 25.0 25.5 26.0 26.5 27.0 27.5 28.0 Temperature (°C)
69
Station 11
Irradiance/PAR (uE m-2 s-1)
0 500 1000 1500 2000 2500 3000 3500 0
20
40
60
Depth (m) 80
100 Irradiance Temperature 120 20 21 22 23 24 25 26 27 28 29
Temperature (°C)
Station 12
Irradiance/PAR (uE m-2 s-1) 0 100 200 300 400 500 600 0
20
40
60
Depth (m) 80
100 Irradiance Temperature 120 20 21 22 23 24 25 26 27 28 29 Temperature (°C)
70
Station 13
Irradiance/PAR (uE m-2 s-1)
0 250 500 750 1000 1250 1500 1750 2000 0
20
40
60
80 (m) Depth
100
120 Irradiance Temperature 140 18 20 22 24 26 28 30 Temperature (°C)
Station 14
Irradiance/PAR (uE m-2 s-1)
0 50 100 150 200 250 300 350 400 0
25
50
75
100 Depth (m) 125
150
175 Irradiance Temperature 200 14 16 18 20 22 24 26 28 Temperature (°C)
71 Appendix D. Deep water CTD profiles by station: mean irradiance/PAR and temperature per 10 m water depth.
Depth Irradiance (μE m-2 s-1) Temperature (°C) Station 1 20 m 122.828 27.598 30 m 61.692 27.594 40 m 32.393 27.526 50 m 16.314 26.227 60 m 8.203 25.396 Station 2 0 m 1311.032 27.594 10 m 357.480 27.594 20 m 203.011 27.596 30 m 109.333 27.551 40 m 56.112 27.033 50 m 28.289 25.586 60 m 14.815 25.314 Station 3 0 m 1526.462 27.640 10 m 560.767 27.639 20 m 308.498 27.640 30 m 159.020 27.635 40 m 93.747 27.014 50 m 46.529 26.328 60 m 23.839 25.429 70 m 13.123 25.352 Station 6 0 m 1673.697 27.744 10 m 641.157 27.732 20 m 356.190 27.741 30 m 206.255 27.756 40 m 118.052 26.161 50 m 59.713 25.924 60 m 29.372 25.752 70 m 15.126 25.689 80 m 8.163 25.357 Station 7 0 m 162.132 27.806 10 m 77.646 27.790 20 m 131.848 27.771 30 m 153.535 27.761 40 m 86.554 26.291 50 m 42.740 25.835 60 m 22.583 25.682 70 m 11.702 25.620 80 m 6.171 25.487 90 m 3.261 23.777 100 m 1.877 21.427 Station 8 0 m 1314.132 27.897 10 m 401.543 27.872 20 m 225.651 27.868 30 m 132.390 27.847
72 40 m 74.336 27.539 50 m 35.794 25.577 60 m 18.349 25.450 70 m 9.390 25.397 80 m 4.985 25.327 90 m 2.697 24.707 100 m 1.504 21.635 110 m 0.890 21.010 Station 9 0 m 678.473 27.648 10 m 206.176 27.654 20 m 106.181 27.655 30 m 59.193 27.655 40 m 33.673 27.499 50 m 17.264 26.821 60 m 9.882 24.935 70 m 5.713 24.130 80 m 3.410 23.184 Station 10 0 m 740.088 27.649 10 m 206.176 27.654 20 m 106.181 27.655 30 m 59.193 27.655 40 m 33.673 27.499 50 m 17.264 26.821 60 m 9.882 24.935 70 m 5.713 24.130 80 m 3.410 23.184 Station 11 0 m 2106.523 27.901 10 m 341.605 27.895 20 m 193.891 27.896 30 m 115.193 27.896 40 m 63.472 27.761 50 m 31.847 26.316 60 m 17.171 24.693 70 m 9.769 23.742 80 m 5.913 22.528 90 m 3.750 21.857 100 m 2.333 21.057 Station 12 0 m 539.060 27.919 10 m 162.170 27.922 20 m 102.080 27.915 30 m 66.796 27.920 40 m 40.651 27.357 50 m 19.851 26.302 60 m 10.075 24.290 70 m 5.628 23.416 80 m 3.226 22.935 90 m 1.933 22.075 100 m 1.217 21.317
73 110 m 0.819 20.412 Station 13 0 m 1663.774 27.831 10 m 430.288 27.774 20 m 227.135 27.764 30 m 118.479 27.754 40 m 64.590 27.689 50 m 28.665 26.515 60 m 13.144 13.144 70 m 7.023 23.493 80 m 3.943 22.072 90 m 4.825 42.998 100 m 1.532 20.708 110 m 1.038 20.651 120 m 0.689 20.571 130 m 0.564 19.505 Station 14 0 m 380.107 27.759 10 m 148.440 27.705 20 m 109.306 27.680 30 m 77.803 27.641 40 m 51.881 26.460 50 m 22.165 24.808 60 m 12.113 23.865 70 m 5.725 22.889 80 m 3.299 21.456 90 m 2.176 20.694 100 m 1.431 20.053 110 m 0.938 19.883 120 m 0.757 19.641 130 m 0.555 19.172 140 m 0.358 18.859 150 m 0.291 17.653 160 m 0.225 16.468 170 m 0.167 15.626 180 m 0.113 14.961
74 Appendix E. Diatom taxa present from Stations 1-14, Onslow Bay, NC.
Stations Species Stations Present Species Present Achnanthes brevipes 4 Fallacia Sp. V 3 Achnanthes delicatula 2,5,8 Fallacia Sp. a 2,5 Achnanthes danica 1,5 Fragilaria brevistriata 2-4,6 Achnanthes hauckiana 1,4,7,10 Fragilaria hyalina 2 Achnanthes Kolbei 1,6 Fragilaria tabulata 3-4,9 Achnanthes manifera 6 Fragilaria Sp. I 1-2 Achnanthes pseudobliqua 3,8 Fragilaria Sp. II 1 Achnanthes reidensis 1-2 Fragilaria Sp. III 1 Achnanthes taeniata 3 Fragilaria Sp. a 1,4-5,7 Achnanthes tenera 1 Grammatophora marina 2-7 Actinoptychus splendens 14 Lyrella Sp. I 3 Amphora beaufortiana 1-2 Mastogloia angusta 1 Amphora coffeaeformis 2-3,7,14 Mastogloia lanceolata 8 Amphora costata 3 Mastogloia pseudoelegans 1 Amphora delicatissima 6 Melosira moniliformis 1-4 Amphora exigua 4-5,9 Navicula abunda 1 Amphora granulata 1-3 Navicula cancellata 2,6 Amphora helenensis 5,7 Navicula digitoconvergens 1 Amphora ovalis 1-4 Navicula diplonoides 1,6 Amphora pannucea 5 Navicula diversestriata 1 Amphora pseudoholsatica 3 Navicula ergadensis 5 Amphora subcuneata 1-2 Navicula Humii 1,7 Amphora tenerrima 2 Navicula menisculus 3,4 Amphora Sp. I 4 Navicula muraliformis 5 Amphora Sp. II 3,6 Navicula nummularia 1,4-6 Amphora Sp. III 2,4 Navicula palpebralis 6,10 Amphora Sp. IV 9 Navicula paul-schulzii 1,4-5 Biddulphia regina 5-6 Navicula reinhardtii 5 Biremis lucens 1-2 Navicula riparia 2,5 Cocconeis californica 1,3,5,6-7,9 Navicula subhamulata 1 Cocconeis convexa 1,6 Navicula Sp. I 1,8,14 Cocconeis dirupta 1-4 Navicula Sp. II 7 Cocconeis disculus 1-10,14 Navicula Sp. III 1,5 Cocconeis distans 1,5-7,14 Nitschia amphibia 3 Cocconeis distantula 1,3,5,8 Nitschia angularis 3,5,8,10 Cocconeis granulifera 2,4 Nitschia brevirostris 2 Cocconeis hoffmanni 1-2,4 Nitschia constricta 4 Cocconeis peltoides 1,5 Nitschia frustulum 1,2,14 Cocconeis pinnata 2,6 Nitschia hybridaeformis 1,3,5,10 Cocconeis placentula 2,10 Nitschia incurva 3,4 Cocconeis scutellum 1-2,4-6 Nitschia marginata 1 Cocconeis Sp. I 1,2,6,10 Nitschia panduriformis 1-10,14 Cocconeis Sp. II 1,2,7 Nitschia Sp. I 1 Cocconeis Sp. III 3-4,6-7,9 Nitschia Sp. II 3-4,7 Cymatosira lorenziana 1,-5,7-8,10 Nitschia Sp. III 7
75 Delphenies karstenii 1,5,10 Odontella aurita 6 Delphenies surirella 1,4,6,10 Opephora pacifica 1-2 Diploneis aestuarii 1-10,14 Parlibellus adnatus 4 Diploneis bombus 5,8,10 Petronies latissima 3 Diploneis chersonensis 4,8,10,14 Pinnularia lanceolata 5 Diploneis decipiens 6,10 Pinnularia Sp. I 4 Diploneis Smithii 7,9 Plagiogramma pygmaeum 1 Entomoneis kjellmanii 1 Pleurosigma distinguendum 5-8,10,14 Eunotogramma marinum 2-7 Pleurosigma marinum 1,6 Eunotogramma rostratum 2-7 Pleurosigma rostratum 3 Fallacia forcipata 7,14 Thallassiosira decipiens 9 Fallacia litoricola 1,4,8 Thallassiosira Sp. I 6 Fallacia plathii 3 Trachysphinia acuminata 1 Fallacia vittata 5 Trachyneis Sp. I 1.5 Fallacia Sp. I 2 Unknown Sp. I 1,3 Fallacia Sp. II 5 Unknown Sp. II 2 Fallacia Sp. III 3 Unknown Sp. III 3 Fallacia Sp. IV 2-3 Unknown Sp. IV 2
Appendix F. Diatom taxa present from Station 1, Onslow Bay, NC.
Achnanthes danica Cocconeis scutellum Navicula diplonoides Achnanthes hauckiana Cocconeis Sp. I Navicula diversestriata Achnanthes Kolbei Cocconeis Sp. II Navicula Humii Achnanthes reidensis Cymatosira lorenziana Navicula nummularia Achnanthes tenera Delphenies karstenii Navicula paul-schulzii Amphora beaufortiana Delphenies surirella Navicula subhamulata Amphora granulata Diploneis aestuarii Navicula Sp. I Amphora ovalis Entomoneis kjellmanii Navicula Sp. III Amphora subcuneata Fallacia litoricola Nitschia frustulum Biremis lucens Fragilaria Sp. I Nitschia hybridaeformis Cocconeis californica Fragilaria Sp. II Nitschia marginata Cocconeis convexa Fragilaria Sp. III Nitschia panduriformis Cocconeis dirupta Fragilaria Sp. a Nitschia Sp. I Cocconeis disculus Mastogloia angusta Opephora pacifica Cocconeis distans Mastogloia pseudoelegans Plagiogramma pygmaeum Cocconeis distantula Melosira moniliformis Pleurosigma marinum Cocconeis hoffmanni Navicula abunda Trachysphinia acuminata Cocconeis peltoides Navicula digitoconvergens Trachyneis Sp. I
76 Appendix G. Diatom taxa present from Station 14, Onslow Bay, NC.
Amphora coffeaformis Cocconeis disculus Cocconeis distans Cocconeis placentula Navicula Sp. a Navicula digitoconvergens Nitschia frustulum Nitschia hybridiformis Nitschia panduriformis
77 Appendix H. Deep water Station 1 morphometric measurements.
Apical Dominant Axis Transapical Ornamentation Species (μm) Axis (μm) Symmetry Raphe Type Ornamentation Index Type 1 Amphora coffeaformis 9 4.25 bilateral biraphid hyaline to complex 2 multiple 2 Amphora coffeaformis 8.75 4 bilateral biraphid hyaline to complex 2 multiple 3 Amphora coffeaformis 9.25 4.5 bilateral biraphid hyaline to complex 2 multiple 4 Cocconeis disculus 17.5 12.25 bilateral monoraphid hyaline to complex 2 unoccluded 5 Cocconeis disculus 8.5 4.75 bilateral monoraphid hyaline to complex 2 unoccluded 6 Cocconeis disculus 8.25 5 bilateral monoraphid hyaline to complex 2 unoccluded 7 Cocconeis disculus 13 7 bilateral monoraphid hyaline to complex 2 unoccluded 8 Cocconeis disculus 7.75 4.75 bilateral monoraphid hyaline to complex 2 unoccluded 9 Cocconeis disculus 8 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 10 Cocconeis disculus 8 5 bilateral monoraphid hyaline to complex 2 unoccluded 11 Cocconeis disculus 6.75 3.75 bilateral monoraphid hyaline to complex 2 unoccluded 12 Cocconeis disculus 11.25 5.75 bilateral monoraphid hyaline to complex 2 unoccluded 13 Cocconeis disculus 7.25 3.5 bilateral monoraphid hyaline to complex 2 unoccluded 14 Cocconeis disculus 9.5 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 15 Cocconeis disculus 12 5.75 bilateral monoraphid hyaline to complex 2 unoccluded 16 Cocconeis disculus 6.25 4 bilateral monoraphid hyaline to complex 2 unoccluded 17 Cocconeis disculus 6.25 3.25 bilateral monoraphid hyaline to complex 2 unoccluded 18 Cocconeis disculus 10 5.25 bilateral monoraphid hyaline to complex 2 unoccluded 19 Cocconeis disculus 11 4.75 bilateral monoraphid hyaline to complex 2 unoccluded 20 Cocconeis disculus 11.75 5.75 bilateral monoraphid hyaline to complex 2 unoccluded 21 Cocconeis disculus 11.5 5.5 bilateral monoraphid hyaline to complex 2 unoccluded 22 Cocconeis disculus 11.5 5.75 bilateral monoraphid hyaline to complex 2 unoccluded 23 Cocconeis disculus 11 5.75 bilateral monoraphid hyaline to complex 2 unoccluded 24 Cocconeis disculus 21.25 13 bilateral monoraphid hyaline to complex 2 unoccluded 25 Cocconeis disculus 10.25 4 bilateral monoraphid hyaline to complex 2 unoccluded 26 Cocconeis disculus 6.75 4 bilateral monoraphid hyaline to complex 2 unoccluded 27 Cocconeis disculus 12.5 6 bilateral monoraphid hyaline to complex 2 volae 28 Cocconeis disculus 17 9.25 bilateral monoraphid hyaline to complex 2 volae
78 29 Cocconeis disculus 16.5 9 bilateral monoraphid hyaline to complex 2 volae 30 Cocconeis disculus 18.5 9.5 bilateral monoraphid hyaline to complex 2 volae 31 Cocconeis disculus 17.5 8 bilateral monoraphid hyaline to complex 2 volae 32 Cocconeis disculus 17.5 8.25 bilateral monoraphid hyaline to complex 2 volae 33 Cocconeis disculus 17.25 8 bilateral monoraphid hyaline to complex 2 volae 34 Cocconeis disculus 17.5 8.25 bilateral monoraphid hyaline to complex 2 volae 35 Cocconeis disculus 9 4 bilateral monoraphid hyaline to complex 2 volae 36 Cocconeis disculus 18 9.25 bilateral monoraphid hyaline to complex 2 volae 37 Cocconeis disculus 13.75 6.5 bilateral monoraphid hyaline to complex 2 volae 38 Cocconeis disculus 21.75 9.5 bilateral monoraphid hyaline to complex 2 volae 39 Cocconeis disculus 15 10 bilateral monoraphid hyaline to complex 2 volae 40 Cocconeis disculus 17 9.25 bilateral monoraphid hyaline to complex 2 volae 41 Cocconeis disculus 12 5.5 bilateral monoraphid hyaline to complex 2 volae 42 Cocconeis disculus 8.5 4.25 bilateral monoraphid hyaline to complex 2 volae 43 Cocconeis disculus 11.5 4.25 bilateral monoraphid hyaline to complex 2 volae 44 Cocconeis disculus 10.25 4 bilateral monoraphid complex 3 hymenate 45 Cocconeis disculus 8.25 4 bilateral monoraphid complex 3 hymenate 46 Cocconeis disculus 9.25 4 bilateral monoraphid complex 3 hymenate 47 Cocconeis disculus 12.75 5.25 bilateral monoraphid complex 3 hymenate 48 Cocconeis disculus 7.75 3.5 bilateral monoraphid complex 3 unoccluded 49 Cocconeis disculus 10 4.5 bilateral monoraphid complex 3 unoccluded 50 Cocconeis disculus 10.75 5 bilateral monoraphid complex 3 unoccluded 51 Cocconeis disculus 11.5 5 bilateral monoraphid complex 3 unoccluded 52 Cocconeis disculus 12.25 5.25 bilateral monoraphid complex 3 unoccluded 53 Cocconeis disculus 8.75 3.75 bilateral monoraphid complex 3 unoccluded 54 Cocconeis disculus 9.75 4 bilateral monoraphid complex 3 unoccluded 55 Cocconeis disculus 10 4.25 bilateral monoraphid complex 3 unoccluded 56 Cocconeis disculus 9 4.5 bilateral monoraphid complex 3 unoccluded 57 Cocconeis disculus 11.5 4.25 bilateral monoraphid complex 3 unoccluded 58 Cocconeis disculus 11 5 bilateral monoraphid complex 3 unoccluded 59 Cocconeis disculus 11.25 5.25 bilateral monoraphid complex 3 unoccluded 60 Cocconeis disculus 10.25 4.75 bilateral monoraphid complex 3 unoccluded
79 61 Cocconeis disculus 8.5 2 bilateral monoraphid complex 3 unoccluded 62 Cocconeis disculus 8 4.25 bilateral monoraphid complex 3 unoccluded 63 Cocconeis disculus 22.5 10 bilateral monoraphid complex 3 unoccluded 64 Cocconeis disculus 9 4.25 bilateral monoraphid complex 3 unoccluded 65 Cocconeis disculus 14.5 7.5 bilateral monoraphid complex 3 unoccluded 66 Cocconeis disculus 10 5.75 bilateral monoraphid hyaline to complex 2 unoccluded 67 Cocconeis disculus 8.75 4 bilateral monoraphid hyaline to complex 2 unoccluded 68 Cocconeis disculus 12 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 69 Cocconeis disculus 11 5.25 bilateral monoraphid complex 3 unoccluded 70 Cocconeis disculus 11 5.5 bilateral monoraphid complex 3 unoccluded 71 Cocconeis disculus 11 5.25 bilateral monoraphid complex 3 unoccluded 72 Cocconeis disculus 11 5.25 bilateral monoraphid complex 3 unoccluded 73 Cocconeis disculus 8.25 4 bilateral monoraphid hyaline to complex 2 unoccluded 74 Cocconeis disculus 12 5 bilateral monoraphid complex 3 unoccluded 75 Cocconeis disculus 13 3.75 bilateral monoraphid complex 3 unoccluded 76 Cocconeis disculus 12 4 bilateral monoraphid complex 3 unoccluded 77 Cocconeis disculus 10.5 5.5 bilateral monoraphid hyaline to complex 2 unoccluded 78 Cocconeis disculus 13.75 9.25 bilateral monoraphid hyaline to complex 2 unoccluded 79 Cocconeis disculus 6.5 3.75 bilateral monoraphid complex 3 unoccluded 80 Cocconeis disculus 10.5 4.25 bilateral monoraphid complex 3 unoccluded 81 Cocconeis disculus 10.5 4 bilateral monoraphid complex 3 unoccluded 82 Cocconeis disculus 13.5 5.75 bilateral monoraphid complex 3 unoccluded 83 Cocconeis disculus 8.5 5 bilateral monoraphid complex 3 multiple 84 Cocconeis disculus 10.25 4 bilateral monoraphid complex 3 multiple 85 Cocconeis disculus 9.5 4.25 bilateral monoraphid complex 3 multiple 86 Cocconeis disculus 9 4 bilateral monoraphid complex 3 multiple 87 Cocconeis disculus 12 5.75 bilateral monoraphid hyaline to complex 2 multiple 88 Cocconeis disculus 8.5 4.5 bilateral monoraphid complex 3 multiple 89 Cocconeis disculus 14.75 13.5 bilateral monoraphid complex 3 multiple 90 Cocconeis disculus 8.5 4 bilateral monoraphid complex 3 multiple 91 Cocconeis disculus 13 4.5 bilateral monoraphid complex 3 multiple 92 Cocconeis disculus 9.75 5 bilateral monoraphid complex 3 multiple
80 93 Cocconeis disculus 15.5 9.75 bilateral monoraphid complex 3 multiple 94 Cocconeis disculus 12.5 5.75 bilateral monoraphid complex 3 multiple 95 Cocconeis disculus 12.5 5.5 bilateral monoraphid complex 3 multiple 96 Cocconeis disculus 12.5 5.5 bilateral monoraphid complex 3 multiple 97 Cocconeis disculus 12.5 5 bilateral monoraphid complex 3 multiple 98 Cocconeis disculus 12.5 5 bilateral monoraphid complex 3 multiple 99 Cocconeis disculus 10.5 4.25 bilateral monoraphid complex 3 multiple 100 Cocconeis disculus 11.5 4.5 bilateral monoraphid complex 3 multiple 101 Cocconeis disculus 9.75 4.5 bilateral monoraphid complex 3 multiple 102 Cocconeis disculus 9.5 4 bilateral monoraphid complex 3 multiple 103 Cocconeis disculus 12 4.75 bilateral monoraphid complex 3 multiple 104 Cocconeis disculus 8.25 4 bilateral monoraphid complex 3 multiple 105 Cocconeis disculus 8.5 4.75 bilateral monoraphid complex 3 multiple 106 Cocconeis disculus 9.25 4.5 bilateral monoraphid complex 3 multiple 107 Cocconeis disculus 8.75 4.25 bilateral monoraphid complex 3 multiple 108 Cocconeis disculus 8.5 5 bilateral monoraphid complex 3 multiple 109 Cocconeis disculus 9.25 4 bilateral monoraphid complex 3 multiple 110 Cocconeis disculus 16.5 12.75 bilateral monoraphid complex 3 unoccluded 111 Cocconeis disculus 11 4 bilateral monoraphid complex 3 multiple 112 Cocconeis disculus 11 4.25 bilateral monoraphid complex 3 multiple 113 Cocconeis disculus 12.5 4.75 bilateral monoraphid complex 3 multiple 114 Cocconeis disculus 14.25 6.5 bilateral monoraphid complex 3 multiple 115 Cocconeis disculus 10.5 5 bilateral monoraphid complex 3 multiple 116 Cocconeis disculus 10 4.25 bilateral monoraphid complex 3 multiple 117 Cocconeis disculus 7 3.75 bilateral monoraphid hyaline to complex 2 unoccluded 118 Cocconeis disculus 8 3.25 bilateral monoraphid hyaline to complex 2 unoccluded 119 Cocconeis disculus 7.25 3.5 bilateral monoraphid hyaline to complex 2 unoccluded 120 Cocconeis disculus 7 3.5 bilateral monoraphid hyaline to complex 2 unoccluded 121 Cocconeis disculus 7.25 3.5 bilateral monoraphid hyaline to complex 2 unoccluded 122 Cocconeis disculus 10.25 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 123 Cocconeis disculus 21 13 bilateral monoraphid hyaline to complex 2 unoccluded 124 Cocconeis disculus 9.25 4.75 bilateral monoraphid hyaline to complex 2 unoccluded
81 125 Cocconeis disculus 9.25 4.75 bilateral monoraphid hyaline to complex 2 unoccluded 126 Cocconeis disculus 7.75 4 bilateral monoraphid hyaline to complex 2 unoccluded 127 Cocconeis disculus 8.75 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 128 Cocconeis disculus 7.25 4 bilateral monoraphid hyaline to complex 2 unoccluded 129 Cocconeis disculus 10.5 4 bilateral monoraphid hyaline to complex 2 unoccluded 130 Cocconeis disculus 14.25 8.5 bilateral monoraphid hyaline to complex 2 unoccluded 131 Cocconeis disculus 13 4.75 bilateral monoraphid hyaline to complex 2 unoccluded 132 Cocconeis disculus 11.25 4 bilateral monoraphid hyaline to complex 2 unoccluded 133 Cocconeis disculus 11.75 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 134 Cocconeis disculus 12.75 5.25 bilateral monoraphid hyaline to complex 2 unoccluded 135 Cocconeis disculus 11.75 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 136 Cocconeis disculus 12.25 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 137 Cocconeis disculus 14 12 bilateral monoraphid hyaline to complex 2 unoccluded 138 Cocconeis disculus 12 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 139 Cocconeis disculus 12 4.75 bilateral monoraphid hyaline to complex 2 unoccluded 140 Cocconeis disculus 13.25 5 bilateral monoraphid hyaline to complex 2 unoccluded 141 Cocconeis disculus 10.25 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 142 Cocconeis disculus 13 4 bilateral monoraphid hyaline to complex 2 unoccluded 143 Cocconeis disculus 7.75 3.75 bilateral monoraphid hyaline to complex 2 unoccluded 144 Cocconeis disculus 14.5 5.75 bilateral monoraphid hyaline to complex 2 unoccluded 145 Cocconeis disculus 19.25 13.75 bilateral monoraphid hyaline to complex 2 unoccluded 146 Cocconeis disculus 19 13.5 bilateral monoraphid hyaline to complex 2 unoccluded 147 Cocconeis disculus 17 12.75 bilateral monoraphid hyaline to complex 2 unoccluded 148 Cocconeis disculus 16 13 bilateral monoraphid hyaline to complex 2 unoccluded 149 Cocconeis disculus 13.5 6.5 bilateral monoraphid hyaline to complex 2 unoccluded 150 Cocconeis disculus 29.25 11.5 bilateral monoraphid hyaline to complex 2 unoccluded 151 Cocconeis disculus 28.5 11.5 bilateral monoraphid hyaline to complex 2 unoccluded 152 Cocconeis disculus 16.25 9.5 bilateral monoraphid hyaline to complex 2 multiple 153 Cocconeis disculus 13.5 9 bilateral monoraphid hyaline to complex 2 multiple 154 Cocconeis disculus 30 9.25 bilateral monoraphid hyaline to complex 2 unoccluded 155 Cocconeis disculus 28 8.5 bilateral monoraphid hyaline to complex 2 unoccluded 156 Cocconeis disculus 31 21.25 bilateral monoraphid complex 3 multiple
82 157 Cocconeis disculus 29.5 8.75 bilateral monoraphid hyaline to complex 2 unoccluded 158 Cocconeis disculus 12 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 159 Cocconeis disculus 18.75 13 bilateral monoraphid hyaline to complex 2 unoccluded 160 Cocconeis disculus 18 12.75 bilateral monoraphid hyaline to complex 2 unoccluded 161 Cocconeis disculus 21.5 10.5 bilateral monoraphid complex 3 multiple 162 Cocconeis disculus 14.25 8.75 bilateral monoraphid complex 3 unoccluded 163 Cocconeis disculus 42.75 19.5 bilateral monoraphid complex 3 unoccluded 164 Cocconeis disculus 37.75 21 bilateral monoraphid hyaline to complex 2 unoccluded 165 Cocconeis disculus 7 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 166 Cocconeis disculus 7 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 167 Cocconeis disculus 7 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 168 Cocconeis disculus 7.5 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 169 Cocconeis disculus 12.25 7.25 bilateral monoraphid hyaline to complex 2 unoccluded 170 Cocconeis disculus 8.5 3.75 bilateral monoraphid hyaline to complex 2 unoccluded 171 Cocconeis distans 39.75 24.5 bilateral monoraphid hyaline to complex 2 unoccluded 172 Cocconeis distans 33.5 19.5 bilateral monoraphid hyaline to complex 2 unoccluded 173 Cocconeis distans 28.25 20 bilateral monoraphid hyaline to complex 2 unoccluded 174 Cocconeis distans 28.75 20.25 bilateral monoraphid hyaline to complex 2 unoccluded 175 Cocconeis distans 40 24.5 bilateral monoraphid hyaline to complex 2 unoccluded 176 Cocconeis distans 37.75 22.75 bilateral monoraphid hyaline to complex 2 unoccluded 177 Cocconeis distans 28.25 20 bilateral monoraphid hyaline to complex 2 unoccluded 178 Cocconeis distans 38 20.5 bilateral monoraphid hyaline to complex 2 unoccluded 179 Cocconeis placentula 10 5.5 bilateral monoraphid complex 3 multiple 180 Cocconeis placentula 10.5 5.5 bilateral monoraphid complex 3 multiple 181 Navicula Sp. I 20 4 bilateral biraphid hyaline to complex 2 hymenate 182 Navicula Sp. I 19.5 4.75 bilateral biraphid hyaline to complex 2 hymenate 183 Navicula Sp. I 18.25 4.5 bilateral biraphid hyaline to complex 2 hymenate 184 Navicula Sp. I 18 4.75 bilateral biraphid hyaline to complex 2 unoccluded 185 Navicula Sp. I 26.5 4.75 bilateral biraphid hyaline to complex 2 unoccluded 186 Nitschia frustulum 6 2.25 bilateral biraphid hyaline to complex 2 unoccluded 187 Nitschia hybridiformis 16.75 2 bilateral biraphid complex 3 none 188 Nitschia panduriformis 18.25 13 bilateral biraphid complex 3 unoccluded
83 189 Nitschia panduriformis 13.5 4.25 bilateral biraphid complex 3 unoccluded 190 Nitschia panduriformis 11.75 4 bilateral biraphid complex 3 unoccluded 191 Nitschia panduriformis 28.75 12.5 bilateral biraphid complex 3 unoccluded 192 Nitschia panduriformis 30 13.75 bilateral biraphid complex 3 unoccluded 193 Nitschia panduriformis 11.5 4.25 bilateral biraphid complex 3 unoccluded 194 Nitschia panduriformis 30 10.25 bilateral biraphid complex 3 unoccluded 195 Nitschia panduriformis 11.75 4.25 bilateral biraphid complex 3 unoccluded 196 Nitschia panduriformis 35 12.5 bilateral biraphid complex 3 unoccluded 197 Nitschia panduriformis 32.25 11.5 bilateral biraphid complex 3 unoccluded 198 Nitschia panduriformis 31.75 12.5 bilateral biraphid complex 3 unoccluded 199 Nitschia panduriformis 26.75 9.75 bilateral biraphid complex 3 unoccluded 200 Nitschia panduriformis 33.5 12 bilateral biraphid complex 3 unoccluded Mean: 14.31 6.91 2.43 Standard Deviation: 7.77 4.49 0.50
Appendix I. Diatom taxa present from Station 14, Onslow Bay, NC.
Amphora coffeaeformis Cocconeis disculus Cocconeis distans Diploneis aestuarii Diploneis chersonensis Navicula Sp. aI Nitschia frustulum Nitschia panduriformis Pleurosigma distinguendum
84 Appendix J. Deep water Station 14 morphometric measurements.
Apical Transapical Dominant Axis Axis Ornamentation Species (μm) (μm) Symmetry Raphe Type Ornamentation Index Type radial 1 Actinoptychus splendens 72 72 discoid araphid complex 3 unoccluded radial 2 Actinoptychus splendens 58.75 58.75 discoid araphid complex 3 unoccluded 3 Cocconeis disculus 11 6 bilateral monoraphid hyaline to complex 2 unoccluded 4 Cocconeis disculus 14.75 9.5 bilateral monoraphid hyaline to complex 2 unoccluded 5 Cocconeis disculus 16.25 8.5 bilateral monoraphid hyaline to complex 2 unoccluded 6 Cocconeis disculus 7.25 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 7 Cocconeis disculus 9.5 5.5 bilateral monoraphid complex 3 unoccluded 8 Cocconeis disculus 9.75 6.5 bilateral monoraphid complex 3 unoccluded 9 Cocconeis disculus 7.25 5 bilateral monoraphid hyaline to complex 2 unoccluded 10 Cocconeis disculus 8 4 bilateral monoraphid hyaline to complex 2 unoccluded 11 Cocconeis disculus 8 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 12 Cocconeis disculus 9.75 4.75 bilateral monoraphid hyaline to complex 2 unoccluded 13 Cocconeis disculus 15.25 11.25 bilateral monoraphid hyaline to complex 2 unoccluded 14 Cocconeis disculus 20 9 bilateral monoraphid hyaline to complex 2 unoccluded 15 Cocconeis disculus 20.25 9.25 bilateral monoraphid complex 3 unoccluded 16 Cocconeis disculus 8 4.25 bilateral monoraphid complex 3 unoccluded 17 Cocconeis disculus 18 12.25 bilateral monoraphid hyaline to complex 2 unoccluded 18 Cocconeis disculus 6.5 4.75 bilateral monoraphid hyaline to complex 2 unoccluded 19 Cocconeis disculus 7.75 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 20 Cocconeis disculus 8.25 5.25 bilateral monoraphid hyaline to complex 2 unoccluded 21 Cocconeis disculus 8.5 6.25 bilateral monoraphid hyaline to complex 2 unoccluded 22 Cocconeis disculus 15.25 7.5 bilateral monoraphid hyaline to complex 2 unoccluded 23 Cocconeis disculus 8.75 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 24 Cocconeis disculus 11.25 7 bilateral monoraphid hyaline to complex 2 unoccluded 25 Cocconeis disculus 15 10.75 bilateral monoraphid hyaline to complex 2 unoccluded 26 Cocconeis disculus 9.25 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 27 Cocconeis disculus 9 4.25 bilateral monoraphid hyaline to complex 2 unoccluded
85 28 Cocconeis disculus 7.25 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 29 Cocconeis disculus 8.25 4 bilateral monoraphid hyaline to complex 2 unoccluded 30 Cocconeis disculus 11.75 7.25 bilateral monoraphid hyaline to complex 2 volae 31 Cocconeis disculus 11.5 5.75 bilateral monoraphid hyaline to complex 2 volae 32 Cocconeis disculus 10 6.75 bilateral monoraphid hyaline to complex 2 volae 33 Cocconeis disculus 11.25 5.5 bilateral monoraphid hyaline to complex 2 volae 34 Cocconeis disculus 13.75 6 bilateral monoraphid hyaline to complex 2 volae 35 Cocconeis disculus 8.75 5.25 bilateral monoraphid hyaline to complex 2 volae 36 Cocconeis disculus 9.5 5.5 bilateral monoraphid hyaline to complex 2 volae 37 Cocconeis disculus 10.75 6.75 bilateral monoraphid hyaline to complex 2 volae 38 Cocconeis disculus 11.25 7 bilateral monoraphid hyaline to complex 2 volae 39 Diploneis chersonensis 33 13.5 bilateral biraphid hyaline to complex 2 unoccluded 40 Diploneis chersonensis 67.25 23.5 bilateral biraphid hyaline to complex 2 unoccluded 41 Diploneis chersonensis 54.5 16.75 bilateral biraphid hyaline to complex 2 unoccluded 42 Nitschia panduriformis 10 3.75 bilateral biraphid complex 3 unoccluded 43 Nitschia panduriformis 10 4 bilateral biraphid complex 3 unoccluded 44 Nitschia panduriformis 10 4.25 bilateral biraphid hyaline to complex 2 unoccluded 45 Nitschia panduriformis 20.25 11.75 bilateral biraphid complex 3 unoccluded 46 Nitschia panduriformis 34.25 18 bilateral biraphid complex 3 unoccluded 47 Nitschia panduriformis 7.75 2.5 bilateral biraphid complex 3 unoccluded 48 Nitschia panduriformis 9.25 2.5 bilateral biraphid complex 3 unoccluded 49 Nitschia panduriformis 19.5 7.75 bilateral biraphid complex 3 unoccluded 50 Nitschia panduriformis 19.75 2.75 bilateral biraphid complex 3 unoccluded 51 Nitschia panduriformis 20 7.75 bilateral biraphid complex 3 unoccluded 52 Nitschia panduriformis 22.5 10 bilateral biraphid complex 3 unoccluded 53 Nitschia panduriformis 25 9.5 bilateral biraphid complex 3 unoccluded 54 Nitschia panduriformis 38 9.5 bilateral biraphid complex 3 unoccluded 55 Nitschia panduriformis 7.5 2.75 bilateral biraphid complex 3 unoccluded 56 Nitschia panduriformis 8 2.25 bilateral biraphid complex 3 unoccluded 57 Nitschia panduriformis 9.5 2.25 bilateral biraphid complex 3 unoccluded
86 58 Nitschia panduriformis 19.5 8.75 bilateral biraphid complex 3 unoccluded 59 Nitschia panduriformis 22.5 7 bilateral biraphid complex 3 unoccluded Mean: 16.87 8.96 2.39 Standard Deviation: 14.46 11.44 0.49
87 Appendix K. Shallow water Station DET-IB taxonomic composition.
Species No. Species No. Species No. Achnanthes conspicua 2 Fragilaria pinnata 14 Nitschia Brittoni 3 Achnanthes hauckiana 5 Fragillaria Sp. a 2 Nitschia calciola 1 Achnanthes longipes 9 Gyrosigma acuminatum 1 Nitschia coarctata 1 Achnanthes tenuis 1 Gyrosigma balticum 3 Nitschia constricta 3 Amphora arenaria 2 Gyrosigma beaufortianum 2 Nitschia frustulum 1 Amphora coffeaeformis 1 Gyrosigma fasciola 2 Nitschia granulata 1 Nitschia Amphora ovalis 24 Gyrosigma simile 1 grossestriata 4 Amphora pseudoholsatica 1 Melosira nummuloides 8 Nitschia järnefeltii 1 Amphora subturgida 12 Navicula agnita 1 Nitschia longa 3 Nitschia Amphora tenerrima 2 Navicula ammophila 2 navicularis 1 Nitschia Amphora ventricosa 16 Navicula Bastowii 16 panduriformis 10 Amphora wisei 1 Navicula cincta 5 Nitschia proxima 1 Amphora Sp. A 1 Navicula directa 4 Nitschia sigma 6 Nitschia Amphora Sp. B 2 Navicula diversistriata 2 valdestriata 1 Amphora Sp. C 2 Navicula eidrigiana 3 Nitschia Sp. A 3 Amphora Sp. D 1 Navicula elginesis 7 Nitschia Sp. C 1 Amphora Sp. E 1 Navicula fenestrella 7 Nitschia Sp. D 1 Bacillaria paxillifer 5 Navicula formenterae 1 Odontella aurita 1 Odontella rhombus form Biddulphia alternans 1 Navicula Hummii 1 trigona 1 Biddulphia pulchella 2 Navicula jeffreyi 1 Opephora marina 7 Campylosira cymbelliformis 1 Navicula menisculus 21 Opephora martyi 20 Opephora Cerataulus radiatus 1 Navicula oculiformis 2 schwartzii 1 Cocconeis disculus 11 Navicula pseudolanceolata 9 Paralia sulcata 6 Plagiogramma Cocconeis distans 4 Navicula pullis 4 Wallichianum 1 Rhopalodia Cocconeis pinnata 12 Navicula rupicola 12 musculus 2 Thallassiosira Cocconeis scutellum 5 Navicula salinarum 17 decipiens 2 Thallassiosira Cyclotella striata 2 Navicula Sovereignae 1 eccentrica 8 Thallassiosira Sp. Delphenies surirella 27 Navicula submitis 2 A 5 Dimeregramma minor 21 Navicula tripunctata 8 Unknown Sp. A 1 Diploneis bombus 4 Navicula Sp. A 3 Unknown Sp. B 2 Diploneis Smithii 1 Navicula Sp. B 1 Unknown Sp. C 1 Diploneis vetula 3 Navicula Sp. C 1 Unknown Sp. D 1 Entomoneis alata 4 Navicula Sp. D 6 Unknown Sp. E 1 Eunotogramma marinum 2 Navicula Sp. E 1 Unknown Sp. F 1 Fallacia forcipata 8 Nitschia amphibia 15 Unknown Sp. G 2 Fallacia litoricola 7 Nitschia angularis 5
88 Appendix L. Shallow water Station DET I-B morphometric measurements.
Apical Dominant Axis Transapical Ornamentation Species (μm) Axis (μm) Symmetry Raphe Type Ornamentation Index Type 1 Amphora arenaria 7 16 bilateral biraphid complex 3 unoccluded 2 Amphora coffeaeformis 42.5 6.75 bilateral biraphid hyaline to complex 2 unoccluded 3 Amphora ovalis 28.5 10.25 bilateral biraphid hyaline to complex 2 unoccluded 4 Amphora ovalis 28.25 14.5 bilateral biraphid hyaline to complex 2 unoccluded 5 Amphora ovalis 24 24.5 bilateral biraphid hyaline to complex 2 unoccluded 6 Amphora similis 12.75 8.25 bilateral biraphid hyaline to complex 2 hymenate 7 Amphora tenerrima 12.25 8 bilateral biraphid hyaline to complex 2 unoccluded 8 Amphora tenerrima 16.25 3.75 bilateral biraphid hyaline to complex 2 multiple 9 Amphora ventricosa 15.25 7.5 bilateral biraphid complex 3 unoccluded 10 Amphora ventricosa 20.75 4 bilateral biraphid complex 3 unoccluded 11 Amphora ventricosa 17.75 3.75 bilateral biraphid complex 3 unoccluded 12 Amphora wisei 14 3.5 bilateral biraphid hyaline to complex 2 unoccluded 13 Amphora Sp. B 30.25 20.25 bilateral biraphid complex 3 unoccluded 14 Amphora Sp. C 19.75 6.25 bilateral biraphid hyaline to complex 2 unoccluded 15 Amphora Sp. D 8 3.75 bilateral biraphid hyaline to complex 2 unoccluded 16 Amphora Sp. E 32.75 6.5 bilateral biraphid hyaline to complex 2 unoccluded 17 Bacillaria paxillifer 66.75 5.75 bilateral biraphid complex 3 hymenate 18 Bacillaria paxillifer 51.25 4.75 bilateral biraphid complex 3 hymenate 19 Bacillaria paxillifer 67.5 4.75 bilateral biraphid complex 3 hymenate 20 Bacillaria paxillifer 64.75 4.75 bilateral biraphid complex 3 hymenate 21 Biddulphia pulchella 46.75 21.75 bilateral araphid complex 3 multiple Campylosira 22 cymbelliformis 19 4.75 radial-cylind araphid complex 3 rotae 23 Cerataulus radiatus 29 29 radial-disc araphid complex 3 unoccluded 24 Cocconeis disculus 23.75 10 bilateral monoraphid hyaline to complex 2 unoccluded 25 Cocconeis disculus 11.75 4.75 bilateral monoraphid hyaline to complex 2 unoccluded 26 Cocconeis disculus 8.5 5.5 bilateral monoraphid hyaline to complex 2 unoccluded 27 Cocconeis disculus 10.25 9.75 bilateral monoraphid hyaline to complex 2 unoccluded
89 28 Cocconeis disculus 10.25 5.5 bilateral monoraphid hyaline to complex 2 hymenate 29 Cocconeis disculus 11.5 5.25 bilateral monoraphid complex 3 hymenate 30 Cocconeis disculus 23 15 bilateral monoraphid complex 3 hymenate 31 Cocconeis pinnata 8.25 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 32 Cyclotella striata 8.75 8.75 radial-cylind araphid hyaline to complex 2 unoccluded 33 Cyclotella striata 13.25 13.25 radial-cylind araphid complex 3 unoccluded 34 Delphenies surirella 13.25 8.5 bilateral araphid hyaline to complex 2 rotae 35 Delphenies surirella 13.75 8.25 bilateral araphid hyaline to complex 2 rotae 36 Delphenies surirella 10.25 8.25 bilateral araphid hyaline to complex 2 rotae 37 Delphenies surirella 8.75 6.25 bilateral araphid hyaline to complex 2 rotae 38 Delphenies surirella 8.25 6.25 bilateral araphid hyaline to complex 2 rotae 39 Delphenies surirella 14.5 8.75 bilateral araphid hyaline to complex 2 rotae 40 Delphenies surirella 21.5 12 bilateral araphid hyaline to complex 2 rotae 41 Delphenies surirella 11.75 8.75 bilateral araphid hyaline to complex 2 rotae 42 Delphenies surirella 9.75 6.25 bilateral araphid hyaline to complex 2 rotae 43 Delphenies surirella 19.75 11.5 bilateral araphid hyaline to complex 2 rotae 44 Delphenies surirella 11.5 8 bilateral araphid hyaline to complex 2 rotae 45 Delphenies surirella 8.75 6 bilateral araphid hyaline to complex 2 rotae 46 Delphenies surirella 5.75 3.25 bilateral araphid hyaline to complex 2 rotae 47 Delphenies surirella 17.5 10 bilateral araphid complex 3 rotae 48 Dimeregramma minor 10.75 8 bilateral araphid hyaline to complex 2 multiple 49 Dimeregramma minor 16.25 6.75 bilateral araphid hyaline to complex 2 multiple 50 Dimeregramma minor 14.25 6.75 bilateral araphid hyaline to complex 2 multiple 51 Dimeregramma minor 15.25 6.25 bilateral araphid hyaline to complex 2 multiple 52 Dimeregramma minor 10.25 6.75 bilateral araphid hyaline to complex 2 multiple 53 Dimeregramma minor 20.5 6.5 bilateral araphid hyaline to complex 2 multiple 54 Dimeregramma minor 10.25 5.75 bilateral araphid hyaline to complex 2 multiple 55 Dimeregramma minor 20.25 9 bilateral araphid hyaline to complex 2 multiple 56 Dimeregramma minor 13.75 7.5 bilateral araphid hyaline to complex 2 multiple 57 Entomoneis alata 16 14.5 bilateral biraphid complex 3 multiple 58 Entomoneis alata 12.75 14.75 bilateral biraphid complex 3 multiple 59 Entomoneis alata 28 17.5 bilateral biraphid complex 3 multiple
90 60 Entomoneis alata 12.25 14.5 bilateral biraphid hyaline to complex 2 hymenate 61 Fallacia forcipata 16 8.25 bilateral biraphid complex 3 unoccluded 62 Fallacia forcipata 16.25 5.75 bilateral biraphid complex 3 unoccluded 63 Fallacia forcipata 32.75 13 bilateral biraphid complex 3 unoccluded 64 Fallacia forcipata 18.75 7.5 bilateral biraphid complex 3 unoccluded 65 Fallacia forcipata 24 8.25 bilateral biraphid complex 3 unoccluded 66 Fallacia forcipata 17.75 7.25 bilateral biraphid complex 3 unoccluded 67 Fallacia forcipata 16.5 8.75 bilateral biraphid complex 3 unoccluded 68 Fallacia litoricola 30 14.5 bilateral biraphid complex 3 unoccluded 69 Fallacia litoricola 17.75 7.5 bilateral biraphid complex 3 unoccluded 70 Fallacia litoricola 16.25 7.75 bilateral biraphid complex 3 unoccluded 71 Fallacia litoricola 16.5 9.25 bilateral biraphid complex 3 unoccluded 72 Fallacia litoricola 17.5 7.75 bilateral biraphid complex 3 unoccluded 73 Fragillaria Sp. a 6.25 6.25 bilateral araphid hyaline to complex 2 unoccluded 74 Fragillaria Sp. a 9.5 3.75 bilateral araphid hyaline to complex 2 unoccluded 75 Gyrosigma acuminatum 126.5 17.5 bilateral biraphid complex 3 unoccluded 76 Gyrosigma balticum 86.25 12.5 bilateral biraphid complex 3 unoccluded 77 Gyrosigma balticum 70.25 10 bilateral biraphid complex 3 unoccluded 78 Gyrosigma balticum 500 45 bilateral biraphid complex 3 unoccluded 79 Gyrosigma beaufortianum 67.5 8 bilateral biraphid complex 3 unoccluded 80 Gyrosigma beaufortianum 70 7.5 bilateral biraphid complex 3 unoccluded 81 Gyrosigma fasciola 93.75 13 bilateral biraphid complex 3 unoccluded 82 Gyrosigma fasciola 83.25 12 bilateral biraphid complex 3 unoccluded 83 Gyrosigma simile 87.5 14.25 bilateral biraphid complex 3 unoccluded 84 Melosira nummuloides 4.25 4.25 radial-cylind araphid complex 3 multiple 85 Melosira nummuloides 4.5 4.5 radial-cylind araphid complex 3 multiple 86 Melosira nummuloides 6.75 6.75 radial-cylind araphid complex 3 multiple 87 Melosira nummuloides 13 13 radial-cylind araphid complex 3 multiple 88 Melosira nummuloides 6 6 radial-cylind araphid complex 3 multiple 89 Melosira nummuloides 8.25 8.25 radial-cylind araphid complex 3 multiple 90 Melosira nummuloides 7 7 radial-cylind araphid complex 3 multiple 91 Melosira nummuloides 7.25 7.25 radial-cylind araphid complex 3 multiple
91 92 Navicula agnita 59.75 11.75 bilateral biraphid hyaline to complex 2 unoccluded 93 Navicula Bastowii 22.75 7.25 bilateral biraphid hyaline to complex 2 unoccluded 94 Navicula Bastowii 21.25 9.75 bilateral biraphid hyaline to complex 2 unoccluded 95 Navicula Bastowii 21.25 9.5 bilateral biraphid hyaline to complex 2 unoccluded 96 Navicula cincta 20.25 3.5 bilateral biraphid complex 3 unoccluded 97 Navicula cincta 12.75 2.25 bilateral biraphid hyaline to complex 2 unoccluded 98 Navicula cincta 17.5 3.75 bilateral biraphid hyaline to complex 2 unoccluded 99 Navicula cincta 20.25 4.25 bilateral biraphid hyaline to complex 2 unoccluded 100 Navicula directa 64.5 9.75 bilateral biraphid complex 3 multiple 101 Navicula directa 54.25 13.25 bilateral biraphid complex 3 multiple 102 Navicula directa 34.5 7.75 bilateral biraphid complex 3 multiple 103 Navicula diversistriata 17.25 10.25 bilateral biraphid complex 3 multiple 104 Navicula eidrigiana 16.75 4.75 bilateral biraphid hyaline to complex 2 unoccluded 105 Navicula eidrigiana 18.75 2.75 bilateral biraphid complex 3 unoccluded 106 Navicula fenestrella 8.25 4.75 bilateral biraphid hyaline to complex 2 hymenate 107 Navicula fenestrella 5.5 3 bilateral biraphid hyaline to complex 2 hymenate 108 Navicula fenestrella 8.75 3.75 bilateral biraphid hyaline to complex 2 hymenate 109 Navicula fenestrella 8.5 5 bilateral biraphid hyaline to complex 2 hymenate 110 Navicula fenestrella 7.75 3.75 bilateral biraphid hyaline to complex 2 hymenate 111 Navicula formenterae 14.25 2.5 bilateral biraphid hyaline to complex 2 unoccluded 112 Navicula jeffreyi 8.25 2.75 bilateral biraphid hyaline to complex 2 hymenate 113 Navicula menisculus 22.5 6.25 bilateral biraphid hyaline to complex 2 unoccluded 114 Navicula menisculus 11.5 5.25 bilateral biraphid hyaline to complex 2 unoccluded 115 Navicula menisculus 20.5 5.5 bilateral biraphid complex 3 unoccluded 116 Navicula menisculus 25 5.5 bilateral biraphid complex 3 unoccluded 117 Navicula menisculus 21 5.25 bilateral biraphid complex 3 unoccluded 118 Navicula menisculus 29.75 7 bilateral biraphid complex 3 unoccluded 119 Navicula oculiformis 15.75 8.25 bilateral biraphid hyaline to complex 2 multiple 120 Navicula oculiformis 18.25 12 bilateral biraphid hyaline to complex 2 multiple 121 Navicula pullus 9 6.75 bilateral biraphid hyaline to complex 2 hymenate 122 Navicula pullus 8.75 4.25 bilateral biraphid hyaline to complex 2 hymenate 123 Navicula pullus 7.5 4.25 bilateral biraphid hyaline to complex 2 hymenate
92 124 Navicula pullus 9 4 bilateral biraphid hyaline to complex 2 multiple 125 Navicula salinarum 27.25 5.75 bilateral biraphid hyaline to complex 2 unoccluded 126 Navicula salinarum 17.5 4.75 bilateral biraphid hyaline to complex 2 unoccluded 127 Navicula salinarum 21.75 5.25 bilateral biraphid hyaline to complex 2 unoccluded 128 Navicula salinarum 12.5 3.75 bilateral biraphid hyaline to complex 2 unoccluded 129 Navicula salinarum 20.75 5 bilateral biraphid hyaline to complex 2 unoccluded 130 Navicula salinarum 17.75 4.75 bilateral biraphid hyaline to complex 2 unoccluded 131 Navicula salinarum 17.75 4.75 bilateral biraphid hyaline to complex 2 unoccluded 132 Navicula salinarum 25.75 5 bilateral biraphid hyaline to complex 2 unoccluded 133 Navicula salinarum 17.75 5 bilateral biraphid hyaline to complex 2 unoccluded 134 Navicula salinarum 14.75 5.5 bilateral biraphid hyaline to complex 2 unoccluded 135 Navicula salinarum 24.75 4.75 bilateral biraphid hyaline to complex 2 unoccluded 136 Navicula salinarum 12.25 4 bilateral biraphid hyaline to complex 2 unoccluded 137 Navicula salinarum 13.75 5 bilateral biraphid hyaline to complex 2 unoccluded 138 Navicula salinarum 18.75 5 bilateral biraphid hyaline to complex 2 unoccluded 139 Navicula salinarum 15.5 6.25 bilateral biraphid hyaline to complex 2 unoccluded 140 Navicula Sp. A 19.5 2.5 bilateral biraphid hyaline to complex 2 unoccluded 141 Navicula Sp. B 15.5 4.5 bilateral biraphid hyaline to complex 2 multiple 142 Navicula Sp. C 6.75 3.75 bilateral biraphid hyaline to complex 2 unoccluded 143 Navicula Sp. a 9 4.25 bilateral biraphid hyaline to complex 2 multiple 144 Navicula Sp. a 8.75 4.25 bilateral biraphid hyaline to complex 2 multiple 145 Navicula Sp. a 5.5 4 bilateral biraphid hyaline to complex 2 multiple 146 Navicula Sp. a 9 4.25 bilateral biraphid hyaline to complex 2 multiple 147 Nitschia amphibia 19.25 2.5 bilateral biraphid complex 3 multiple 148 Nitschia amphibia 21.75 2.75 bilateral biraphid complex 3 multiple 149 Nitschia amphibia 9.5 2.25 bilateral biraphid complex 3 multiple 150 Nitschia amphibia 30.75 4.25 bilateral biraphid complex 3 multiple 151 Nitschia amphibia 12.25 2 bilateral biraphid complex 3 multiple 152 Nitschia amphibia 6.5 2.25 bilateral biraphid hyaline to complex 2 hymenate 153 Nitschia amphibia 6.25 2 bilateral biraphid hyaline to complex 2 hymenate 154 Nitschia Brittoni 25.5 5 bilateral biraphid complex 3 multiple 155 Nitschia Brittoni 41.15 10.5 bilateral biraphid complex 3 multiple
93 156 Nitschia Brittoni 33.25 10 bilateral biraphid complex 3 multiple 157 Nitschia calciola 25 5 bilateral biraphid complex 3 multiple 158 Nitschia coarctata 22.75 9 bilateral biraphid complex 3 multiple 159 Nitschia constricta 32.75 10.25 bilateral biraphid complex 3 multiple 160 Nitschia constricta 36.75 5.5 bilateral biraphid complex 3 multiple 161 Nitschia frustulum 21.25 4.25 bilateral biraphid complex 3 hymenate 162 Nitschia grossestriata 51.75 8.5 bilateral biraphid complex 3 unoccluded 163 Nitschia grossestriata 50.25 8.5 bilateral biraphid complex 3 unoccluded 164 Nitschia grossestriata 38.25 9.5 bilateral biraphid complex 3 unoccluded 165 Nitschia longa 61.25 5 bilateral biraphid complex 3 hymenate 166 Nitschia navicularis 32.75 7.5 bilateral biraphid complex 3 unoccluded 167 Nitschia panduriformis 24.25 8.5 bilateral biraphid complex 3 unoccluded 168 Nitschia panduriformis 22.25 7.5 bilateral biraphid complex 3 unoccluded 169 Nitschia panduriformis 27.5 10.5 bilateral biraphid complex 3 unoccluded 170 Nitschia panduriformis 33.25 15 bilateral biraphid complex 3 unoccluded 171 Nitschia panduriformis 7.25 3.75 bilateral biraphid complex 3 unoccluded 172 Nitschia panduriformis 9.75 4.25 bilateral biraphid complex 3 unoccluded 173 Nitschia proxima 40.25 3.5 bilateral biraphid complex 3 hymenate 174 Nitschia sigma 38.75 3 bilateral biraphid complex 3 hymenate 175 Nitschia sigma 65 7.5 bilateral biraphid complex 3 unoccluded 176 Nitschia valdestriata 12.75 4.75 bilateral biraphid complex 3 hymenate 177 Nitschia Sp. A 62.25 8.5 bilateral biraphid hyaline to complex 2 unoccluded 178 Nitschia Sp. B 33.25 10.25 bilateral biraphid hyaline to complex 2 unoccluded 179 Odontella aurita 17.5 25 bilateral araphid complex 3 multiple 180 Odontella rhombus 38 38 bilateral araphid complex 3 unoccluded 181 Opephora marina 13.5 2.5 bilateral araphid hyaline to complex 2 multiple 182 Opephora marina 11.75 2.5 bilateral araphid hyaline to complex 2 multiple 183 Opephora marina 12.25 2.5 bilateral araphid hyaline to complex 2 multiple 184 Opephora martyii 13.25 4.25 bilateral araphid complex 3 cribera 185 Opephora martyii 7.75 4 bilateral araphid complex 3 cribera 186 Opephora martyii 6.75 4 bilateral araphid complex 3 cribera 187 Opephora martyii 9.25 4.5 bilateral araphid complex 3 cribera
94 188 Opephora martyii 17.25 5.25 bilateral araphid complex 3 cribera 189 Opephora martyii 5.75 2.25 bilateral araphid hyaline to complex 2 cribera 190 Opephora martyii 8.75 3.75 bilateral araphid complex 3 cribera 191 Paralia sulcata 22.5 22.5 radial-cylind araphid hyaline 1 none 192 Plagiogramma Wallichianum 33.25 7 bilateral araphid complex 3 multiple 193 Thallassiosira deipiens 11.75 11.75 radial-disc araphid complex 3 unoccluded 194 Thallassiosira Sp. A 14.75 14.75 radial-disc araphid complex 3 unoccluded 195 Thallassiosira Sp. A 4 4 radial-disc araphid complex 3 unoccluded 196 Unknown Sp. C 21.25 21.25 bilateral araphid complex 3 unoccluded 197 Unknown Sp. D 12.75 4.25 radial cylind araphid hyaline to complex 2 none 198 Unknown Sp. E 7 7 radial cylind araphid complex 3 hymenate 199 Unknown Sp. F 11.75 11.75 radial cylind araphid complex 3 multiple 200 Unknown Sp. G 11.25 11.25 bilateral araphid hyaline to complex 2 unoccluded Mean: 24.79 7.87 2.50 Standard Deviation: 38.71 5.70 0.51
95 Appendix M. Shallow water Station ND IV-D taxonomic composition.
Species No. Species No. Species No. Achnanthes conspicua 1 Eunotogramma laea 1 Navicula tripunctata 3 Achnanthes hauckiana 1 Eunotogramma marinum 3 Navicula Sp. E 1 Eunotogramma Achnanthes longipes 1 rostratum 3 Navicula Sp. G 4 Actinoptychus splendens 2 Fallacia forcipata 3 Navicula Sp. a 6 Amphora arenaria 1 Fallacia litoricola 9 Nitschia amphibia 23 Amphora grannulata 4 Gyrosigma balticum 2 Nitschia angularis 2 Gyrosigma Amphora ovalis 8 beaufortianum 4 Nitschia Brittoni 3 Amphora subturgida 3 Gyrosigma fasciola 2 Nitschia coarctata 7 Amphora tenerrima 3 Gyrosigma simile 3 Nitschia frustulum 1 Nitschia Amphora ventricosa 4 Melosira nummuloides 37 grossestriata 3 Amphora Sp. A 3 Navicula agnita 1 Nitschia longa 5 Amphora Sp. B 1 Navicula ammophila 6 Nitschia navicularis 3 Nitschia Amphora Sp. D 3 Navicula Bastowii 10 panduriformis 22 Bacillaria paxillifer 4 Navicula cincta 3 Nitschia proxima 1 Campylosira cymbelliformis 1 Navicula directa 9 Nitschia sigma 6 Nitschia Cocconeis disculoides 1 Navicula diversistriata 2 sigmaformis 1 Cocconeis disculus 16 Navicula elginensis 4 Nitschia valdestriata 1 Cocconeis distans 3 Navicula fenestrella 14 Nitschia Sp. A 1 Cocconeis guttata 1 Navicula formenterae 2 Odontella aurita 1 Cocconeis pinnata 7 Navicula Hummii 9 Opephora marina 10 Cocconeis placentula 1 Navicula jeffreyi 2 Opephora martyi 15 Cocconeis scutellum 5 Navicula menisculus 5 Paralia sulcata 18 Plagiogramma Coscinodiscus devius 2 Navicula misella 1 pygmaeum 2 Pleurosigma Cyclotella striata 12 Navicula pennata 1 distinguendum 2 Navicula Rhopalodia Cymatosira lorenziana 2 pseudolanceolata 8 musculus 1 Thalassiosira Delphenies surirella 23 Navicula pullus 1 decipiens 13 Thalassiosira Dimeregramma minor 14 Navicula restituta 3 eccentrica 2 Diploneis bombus 5 Navicula rupicola 1 Thalassiosira Sp. A 9 Thalassiosira Diploneis Smithii 3 Navicula salinarum 46 weissflogii 1 Entomoneis alata 2 Navicula Sovereignae 1
96 Appendix N. Shallow water Station ND IV-D morphometric measurements.
Apical Dominant Axis Transapical Ornamentation Species (μm) Axis (μm) Symmetry Raphe Type Ornamentation Index Type 1 Amphiprora similis 72.75 23 bilateral biraphid complex 3 multiple 2 Amphora grannulata 35.5 14 bilateral biraphid hyaline to complex 2 unoccluded 3 Amphora grannulata 21 7.5 bilateral biraphid hyaline to complex 2 unoccluded 4 Amphora grannulata 30 14.5 bilateral biraphid hyaline to complex 2 unoccluded 5 Amphora grannulata 20 6.75 bilateral biraphid hyaline to complex 2 unoccluded 6 Amphora ovalis 23.25 12.5 bilateral biraphid hyaline to complex 2 unoccluded 7 Amphora ovalis 10.75 12 bilateral biraphid hyaline to complex 2 unoccluded 8 Amphora ovalis 11.25 4.25 bilateral biraphid hyaline to complex 2 unoccluded 9 Amphora ovalis 30.5 12.75 bilateral biraphid hyaline to complex 2 unoccluded 10 Amphora tenerrima 9.75 3.75 bilateral biraphid hyaline to complex 2 multiple 11 Amphora tenerrima 18.25 13 bilateral biraphid hyaline to complex 2 multiple 12 Amphora Sp. D 11.25 4.5 bilateral biraphid hyaline to complex 2 unoccluded 13 Amphora Sp. D 11.25 4.5 bilateral biraphid hyaline to complex 2 unoccluded 14 Cocconeis disculoides 36.25 17 bilateral monoraphid complex 3 unoccluded 15 Cocconeis disculus 12.5 5.5 bilateral monoraphid hyaline to complex 2 unoccluded 16 Cocconeis disculus 11 5.75 bilateral monoraphid hyaline to complex 2 unoccluded 17 Cocconeis disculus 12.5 6.5 bilateral monoraphid hyaline to complex 2 unoccluded 18 Cocconeis distans 25 14.75 bilateral monoraphid hyaline to complex 2 unoccluded 19 Cocconeis guttata 7.75 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 20 Cocconeis pinnata 10.5 4.5 bilateral monoraphid hyaline to complex 2 unoccluded 21 Cocconeis pinnata 9.75 4.25 bilateral monoraphid hyaline to complex 2 unoccluded 22 Cocconeis pinnata 11.5 3.75 bilateral monoraphid hyaline to complex 2 unoccluded 23 Cocconeis pinnata 7.25 3.5 bilateral monoraphid hyaline to complex 2 unoccluded 24 Cococneis pinnata 9.75 3.75 bilateral monoraphid hyaline to complex 2 unoccluded 25 Coscinodiscus devius 19.25 19.25 radial/disc araphid complex 3 unoccluded 26 Cyclotella meneghiniana 17.75 17.75 radial/cylind araphid hyaline to complex 2 multiple 27 Cyclotella meneghiniana 20.5 20.5 radial/cylind araphid hyaline to complex 2 multiple 28 Cyclotella meneghiniana 28.25 28.25 radial/cylind araphid hyaline to complex 2 multiple
97 29 Cyclotella striata 28.75 28.75 radial/cylind araphid hyaline to complex 2 unoccluded 30 Cyclotella striata 12.5 12.5 radial/cylind araphid hyaline to complex 2 unoccluded 31 Delphenies surirella 12.25 6 bilateral araphid hyaline to complex 2 rotae 32 Delphenies surirella 13.75 7 bilateral araphid hyaline to complex 2 rotae 33 Delphenies surirella 3.25 9 bilateral araphid hyaline to complex 2 rotae 34 Delphenies surirella 9.25 5 bilateral araphid hyaline to complex 2 rotae 35 Delphenies surirella 11.5 6.25 bilateral araphid hyaline to complex 2 rotae 36 Delphenies surirella 11.75 4.25 bilateral araphid hyaline to complex 2 rotae 37 Delphenies surirella 6.75 6.25 bilateral araphid hyaline to complex 2 rotae 38 Delphenies surirella 7.75 5 bilateral araphid hyaline to complex 2 rotae 39 Delphenies surirella 11.75 5.75 bilateral araphid hyaline to complex 2 rotae 40 Delphenies surirella 12.25 6 bilateral araphid hyaline to complex 2 rotae 41 Delphenies surirella 13.5 4.75 bilateral araphid hyaline to complex 2 rotae 42 Delphenies surirella 7.5 3.75 bilateral araphid hyaline to complex 2 rotae 43 Delphenies surirella 12 9.5 bilateral araphid hyaline to complex 2 rotae 44 Delphenies surirella 17 6 bilateral araphid hyaline to complex 2 rotae 45 Delphenies surirella 12.5 8.5 bilateral araphid hyaline to complex 2 rotae 46 Dimeregramma minor 18.25 3.5 bilateral araphid hyaline to complex 2 multiple 47 Diploneis bombus 54.5 13.75 bilateral biraphid hyaline to complex 2 multiple 48 Diploneis smithii 18.25 5.75 bilateral biraphid hyaline to complex 2 volae 49 Gyrosigma balticum 155 23.25 bilateral biraphid complex 3 unoccluded 50 Gyrosigma beafortianum 60.25 6.5 bilateral biraphid complex 3 unoccluded 51 Gyrosigma beaufortianum 97 10.25 bilateral biraphid complex 3 unoccluded 52 Gyrosigma beaufortianum 67 7.25 bilateral biraphid complex 3 unoccluded 53 Gyrosigma beaufortianum 57 6 bilateral biraphid complex 3 unoccluded 54 Gyrosigma fasciola 75.5 8.75 bilateral biraphid complex 3 unoccluded 55 Gyrosigma fasciola 93.75 9.75 bilateral biraphid complex 3 unoccluded 56 Gyrosigma simile 86.75 12.5 bilateral biraphid complex 3 unoccluded 57 Gyrosigma simile 95.5 11 bilateral biraphid complex 3 unoccluded 58 Melosira nummuloides 20 20 radial/cylind araphid complex 3 multiple 59 Melosira nummuloides 9.25 9.25 radial/cylind araphid complex 3 multiple 60 Melosira nummuloides 11 11 radial/cylind araphid complex 3 multiple
98 61 Melosira nummuloides 8.75 8.75 radial/cylind araphid complex 3 multiple 62 Melosira nummuloides 11.25 11.25 radial/cylind araphid complex 3 multiple 63 Melosira nummuloides 13 13 radial/cylind araphid complex 3 multiple 64 Melosira nummuloides 9.75 9.75 radial/cylind araphid complex 3 multiple 65 Melosira nummuloides 8.75 8.75 radial/cylind araphid complex 3 multiple 66 Melosira nummuloides 9.5 9.5 radial/cylind araphid complex 3 multiple 67 Melosira nummuloides 8.75 8.75 radial/cylind araphid complex 3 multiple 68 Melosira nummuloides 8 8 radial/cylind araphid complex 3 multiple 69 Melosira nummuloides 6.75 6.75 radial/cylind araphid complex 3 multiple 70 Melosira nummuloides 9 9 radial/cylind araphid complex 3 multiple 71 Melosira nummuloides 11.75 11.75 radial/cylind araphid complex 3 multiple 72 Melosira nummuloides 8.75 8.75 radial/cylind araphid complex 3 multiple 73 Melosira nummuloides 10.25 10.25 radial/cylind araphid complex 3 multiple 74 Melosira nummuloides 10.5 10.5 radial/cylind araphid complex 3 multiple 75 Melosira nummuloides 11.5 11.5 radial/cylind araphid complex 3 multiple 76 Melosira nummuloides 11.25 11.25 radial/cylind araphid complex 3 multiple 77 Melosira nummuloides 13.5 13.5 radial/cylind araphid complex 3 multiple 78 Melosira nummuloides 8.75 8.75 radial/cylind araphid complex 3 multiple 79 Navicula directa 62.5 10.5 bilateral biraphid complex 3 multiple 80 Navicula fenestrella 10.75 4.75 bilateral biraphid hyaline to complex 2 hymenate 81 Navicula fenestrella 15.5 3 bilateral biraphid hyaline to complex 2 hymenate 82 Navicula fenestrella 10.25 4.25 bilateral biraphid hyaline to complex 2 hymenate 83 Navicula fenestrella 7.75 4.25 bilateral biraphid hyaline to complex 2 hymenate 84 Navicula fenestrella 9.5 4.5 bilateral biraphid hyaline to complex 2 hymenate 85 Navicula forcipata 29.25 10.25 bilateral biraphid complex 3 unoccluded 86 Navicula forcipata 15.25 7.5 bilateral biraphid complex 3 unoccluded 87 Navicula Humii 16.75 10.25 bilateral biraphid hyaline to complex 2 unoccluded 88 Navicula jeffreyi 9.25 2 bilateral biraphid hyaline to complex 2 hymenate 89 Navicula jeffreyi 9.25 2.5 bilateral biraphid hyaline to complex 2 hymenate 90 Navicula litoricola 23 9 bilateral biraphid complex 3 unoccluded 91 Navicula litoricola 20.5 8.5 bilateral biraphid complex 3 unoccluded 92 Navicula litoricola 19.5 7.75 bilateral biraphid complex 3 unoccluded
99 93 Navicula litoricola 21.25 9.75 bilateral biraphid complex 3 unoccluded 94 Navicula litoricola 17 8.25 bilateral biraphid complex 3 unoccluded 95 Navicula litoricola 25.25 9.25 bilateral biraphid complex 3 unoccluded 96 Navicula menisculus 12.25 4.5 bilateral biraphid hyaline to complex 2 unoccluded 97 Navicula misella 18.25 5.5 bilateral biraphid hyaline to complex 2 unoccluded 98 Navicula pennata 29 13.5 bilateral biraphid complex 3 multiple 99 Navicula pseudolanceolata 28.5 10.5 bilateral biraphid hyaline to complex 2 unoccluded 100 Navicula pseudolanceolata 18.5 6 bilateral biraphid hyaline to complex 2 unoccluded 101 Navicula restituta 36 7.5 bilateral biraphid complex 3 unoccluded 102 Navicula restituta 24 8.5 bilateral biraphid complex 3 unoccluded 103 Navicula restituta 27 10 bilateral biraphid complex 3 unoccluded 104 Navicula salinarum 16.5 5.25 bilateral biraphid hyaline to complex 2 unoccluded 105 Navicula salinarum 19.5 4 bilateral biraphid hyaline to complex 2 unoccluded 106 Navicula salinarum 12 2.5 bilateral biraphid hyaline to complex 2 unoccluded 107 Navicula salinarum 16 3.5 bilateral biraphid hyaline to complex 2 unoccluded 108 Navicula salinarum 15.5 3 bilateral biraphid hyaline to complex 2 unoccluded 109 Navicula salinarum 13.25 2.5 bilateral biraphid hyaline to complex 2 unoccluded 110 Navicula salinarum 15.5 4 bilateral biraphid hyaline to complex 2 unoccluded 111 Navicula salinarum 16.5 3 bilateral biraphid hyaline to complex 2 unoccluded 112 Navicula salinarum 19.5 3.5 bilateral biraphid hyaline to complex 2 unoccluded 113 Navicula salinarum 19.25 4 bilateral biraphid hyaline to complex 2 unoccluded 114 Navicula salinarum 18.25 4.75 bilateral biraphid hyaline to complex 2 unoccluded 115 Navicula salinarum 17 5 bilateral biraphid hyaline to complex 2 unoccluded 116 Navicula salinarum 21.75 4.25 bilateral biraphid hyaline to complex 2 unoccluded 117 Navicula salinarum 18 4.25 bilateral biraphid hyaline to complex 2 unoccluded 118 Navicula salinarum 19 4.75 bilateral biraphid hyaline to complex 2 unoccluded 119 Navicula salinarum 19.5 3.75 bilateral biraphid hyaline to complex 2 unoccluded 120 Navicula salinarum 19 3.75 bilateral biraphid hyaline to complex 2 unoccluded 121 Navicula salinarum 16.75 4 bilateral biraphid hyaline to complex 2 unoccluded 122 Navicula salinarum 17.75 4.75 bilateral biraphid hyaline to complex 2 unoccluded 123 Navicula salinarum 21 5 bilateral biraphid hyaline to complex 2 unoccluded 124 Navicula salinarum 9.75 2.25 bilateral biraphid hyaline to complex 2 unoccluded
100 125 Navicula salinarum 13 4 bilateral biraphid hyaline to complex 2 unoccluded 126 Navicula salinarum 15.75 4.75 bilateral biraphid hyaline to complex 2 unoccluded 127 Navicula salinarum 16 4 bilateral biraphid hyaline to complex 2 unoccluded 128 Navicula salinarum 12.5 2.5 bilateral biraphid hyaline to complex 2 unoccluded 129 Navicula salinarum 14.5 3.75 bilateral biraphid hyaline to complex 2 unoccluded 130 Navicula salinarum 18.5 5 bilateral biraphid hyaline to complex 2 unoccluded 131 Navicula salinarum 15.75 5.25 bilateral biraphid hyaline to complex 2 unoccluded 132 Navicula salinarum 23.75 5.25 bilateral biraphid hyaline to complex 2 unoccluded 133 Navicula salinarum 19.5 4.75 bilateral biraphid hyaline to complex 2 unoccluded 134 Navicula salinarum 21 5.5 bilateral biraphid hyaline to complex 2 unoccluded 135 Navicula salinarum 12.5 2.25 bilateral biraphid hyaline to complex 2 unoccluded 136 Navicula salinarum 12.5 2.25 bilateral biraphid hyaline to complex 2 unoccluded 137 Navicula salinarum 12.75 2.5 bilateral biraphid hyaline to complex 2 unoccluded 138 Navicula tripunctata 59.75 7.5 bilateral biraphid hyaline to complex 2 unoccluded 139 Navicula tripunctata 36.75 7 bilateral biraphid hyaline to complex 2 unoccluded 140 Navicula Sp. A 36 7.5 bilateral biraphid hyaline to complex 2 unoccluded 141 Navicula Sp. E 9.75 3.75 bilateral biraphid hyaline to complex 2 unoccluded 142 Navicula Sp. F 33.75 7.25 bilateral biraphid complex 3 unoccluded 143 Navicula Sp. F 36.25 6.5 bilateral biraphid complex 3 unoccluded 144 Navicula Sp. F 26.25 5.5 bilateral biraphid complex 3 unoccluded 145 Navicula Sp. G 60 13.5 bilateral biraphid complex 3 unoccluded 146 Navicula Sp. G 75.5 7.5 bilateral biraphid complex 3 unoccluded 147 Navicula Sp. G 65.75 13.5 bilateral biraphid complex 3 unoccluded 148 Navicula Sp. G 30.25 5.25 bilateral biraphid complex 3 unoccluded 149 Navicula Sp. a 7.25 3.75 bilateral biraphid hyaline to complex 2 multiple 150 Navicula Sp. a 7.5 4.25 bilateral biraphid hyaline to complex 2 multiple 151 Navicula Sp. a 5.5 3.75 bilateral biraphid hyaline to complex 2 multiple 152 Navicula Sp. a 6.75 4 bilateral biraphid hyaline to complex 2 multiple 153 Navicula Sp. a 9.75 5 bilateral biraphid hyaline to complex 2 multiple 154 Nitschia amphibia 27.75 3.5 bilateral biraphid complex 3 multiple 155 Nitschia amphibia 9.25 2.5 bilateral biraphid complex 3 multiple 156 Nitschia amphibia 8.25 2.25 bilateral biraphid complex 3 multiple
101 157 Nitschia amphibia 9.75 4 bilateral biraphid complex 3 multiple 158 Nitschia amphibia 21.75 3 bilateral biraphid complex 3 multiple 159 Nitschia amphibia 7.75 1.75 bilateral biraphid hyaline to complex 2 unoccluded 160 Nitschia Brittoni 14.5 4.25 bilateral biraphid complex 3 multiple 161 Nitschia Brittoni 52 9.75 bilateral biraphid complex 3 multiple 162 Nitschia coarctata 21.25 9.5 bilateral biraphid complex 3 multiple 163 Nitschia coarctata 19.75 7.5 bilateral biraphid complex 3 multiple 164 Nitschia coarctata 27.5 9 bilateral biraphid complex 3 multiple 165 Nitschia coarctata 21.75 9.75 bilateral biraphid complex 3 multiple 166 Nitschia coarctata 19.75 5.25 bilateral biraphid complex 3 multiple 167 Nitschia coarctata 39.75 10 bilateral biraphid complex 3 multiple 168 Nitschia coarctata 19.75 9.5 bilateral biraphid complex 3 multiple 169 Nitschia frustulum 23.5 2.75 bilateral biraphid hyaline to complex 2 hymenate 170 Nitschia grossestriata 21 4.5 bilateral biraphid complex 3 unoccluded 171 Nitschia navicularis 36 6.5 bilateral biraphid complex 3 unoccluded 172 Nitschia navicularis 38 7.25 bilateral biraphid complex 3 unoccluded 173 Nitschia navicularis 46 4 bilateral biraphid complex 3 unoccluded 174 Nitschia panduriformis 21 4.75 bilateral biraphid complex 3 unoccluded 175 Nitschia panduriformis 8.5 4.75 bilateral biraphid hyaline to complex 2 hymenate 176 Nitschia panduriformis 7.25 5.25 bilateral biraphid hyaline to complex 2 hymenate 177 Nitschia panduriformis 4.75 3 bilateral biraphid hyaline to complex 2 hymenate 178 Nitschia sigmaformis 104 8 bilateral biraphid complex 3 unoccluded 179 Nitschia valdestriata 7.25 3.75 bilateral biraphid complex 3 hymenate 180 Nitschia Sp. a 15 5.25 bilateral biraphid complex 3 unoccluded 181 Nitschia Sp. E 46.5 8.75 bilateral biraphid complex 3 unoccluded 182 Nitschia Sp. E 45.25 2.25 bilateral biraphid complex 3 unoccluded 183 Nitschia Sp. E 92.25 2 bilateral biraphid complex 3 unoccluded 184 Odontella aurita 43.25 17.75 bilateral araphid complex 3 multiple 185 Opephora marina 10.25 2.25 bilateral araphid hyaline to complex 2 multiple 186 Opephora martyii 6 2.25 bilateral araphid complex 3 cribera 187 Opephora martyii 8.75 3.25 bilateral araphid complex 3 cribera 188 Opephora martyii 7.25 3 bilateral araphid complex 3 cribera
102 189 Pleurosigma distinguendum 65.25 10.5 bilateral biraphid complex 3 unoccluded 190 Pleurosigma distinguendum 64.5 5.75 bilateral biraphid complex 3 unoccluded 191 Rhopalodia musculus 10 6.5 bilateral biraphid complex 3 multiple 192 Thalassiosira decipiens 10 10 radial/cylind araphid complex 3 unoccluded 193 Thalassiosira decipiens 10 10 radial/cylind araphid complex 3 unoccluded 194 Thalassiosira decipiens 7.25 7.25 radial/cylind araphid complex 3 unoccluded 195 Thalassiosira decipiens 4.25 4.25 radial/cylind araphid complex 3 unoccluded 196 Thalassiosira decipiens 5 5 radial/cylind araphid complex 3 unoccluded 197 Thalassiosira weissflogii 19.75 19.75 radial/cylind araphid complex 3 unoccluded 198 Thalassiosira Sp. A 3.75 3.75 radial/cylind araphid complex 3 unoccluded 199 Thalassiosira Sp. A 4.5 4.5 radial/cylind araphid complex 3 unoccluded 200 Thalassiosira Sp. A 4.75 4.75 radial/cylind araphid complex 3 unoccluded Mean: 22.81 7.36 2.47 Standard Deviation: 21.85 4.69 0.50
103 Appendix O. Deep water and shallow water diatom surface area to volume ratios, by species.
Cocconeis disculus Apical Axis Transapical Axis Pervalvar axis Deep water Stations (μm) (μm) (μm) S/V Ratio 1 5.25 4.25 1 1.000 1 6.75 2.25 1 1.000 1 7.25 5 1.5 0.667 1 8 4 1.75 0.571 1 8 4.25 1.5 0.667 1 9.75 5 1.5 0.667 1 11.5 5.5 2.5 0.400 1 15.25 11 2.5 0.400 1 20 9 3 0.333 1 20.5 9.25 3.25 0.308 9 8 4.25 1.5 0.667 9 18 12.5 3.5 0.286 14 6.5 4.75 1.5 0.667 14 7.75 4.25 1.25 0.800 14 8.25 5.25 1.25 0.800 14 8.25 6.25 1.75 0.571 14 10 6.75 1.75 0.571 14 15 7.75 2.25 0.444 14 15.25 9.75 1.75 0.571 14 19.25 8.25 2.25 0.444 Mean: 0.592 Shallow water Stations IB 7.5 4.25 1.25 0.800 IB 8 5.75 1.5 0.667 IB 8 4.5 1.25 0.800 IB 9.5 5.5 1.5 0.667 IB 9.5 6 1.5 0.667 IB 9.75 6.75 1.75 0.571 IB 12.5 5.5 2 0.500 IB 12.75 6.75 2.25 0.444 IB 15.5 2.5 2 0.500 IB 20.25 15.25 3 0.333 IV 7.5 4 1.5 0.667 IV 9.25 6.25 1.75 0.571 IV 10.25 8 2 0.500 IV 10.5 5.5 1.75 0.571 IV 10.75 5.25 1.25 0.800 IV 11.75 6.5 1.5 0.667 IV 12.5 5.25 2 0.500 IV 16.5 2.25 2 0.500 IV 23 11.25 2.25 0.444 IV 23.5 10.75 2.5 0.400 Mean: 0.578
104 Fallacia forcipata Deep water Apical Axis Transapical Axis Pervalvar axis Stations (μm) (μm) (μm) S/V Ratio 1 15.5 6.25 4 0.250 1 16.5 9.5 4.25 0.235 1 18.25 10.25 4 0.250 1 25.75 9.5 4.5 0.222 1 29 12.5 4.5 0.222 1 30 12.5 4.5 0.222 1 32.25 12.75 4.75 0.211 1 33.25 13.5 4.5 0.222 1 33.5 13.75 4.75 0.211 1 35.75 15 4.75 0.211 5 16.75 6.5 4.25 0.235 5 31.5 12.25 4.5 0.222 5 33.25 13.75 4.5 0.222 7 37.75 15.25 4.75 0.211 7 38.5 16.5 4.75 0.211 8 15.75 6.5 4 0.250 8 31.25 12.5 4.5 0.222 8 35 14.5 4.75 0.211 9 17 9.75 4.25 0.235 14 24.5 9.25 4.5 0.222 Mean: 0.225 Shallow water Stations IB 16.25 5.75 4.25 0.235 IB 16.75 6.5 4 0.250 IB 17.5 7.5 4 0.250 IB 18.25 6.75 4.25 0.235 IB 18.5 7.25 4 0.250 IB 18.75 7.5 4 0.250 IB 22.5 7.5 4.25 0.235 IB 24 8.25 4.25 0.235 IB 32.75 13 4.5 0.222 IB 33.5 13.25 4.5 0.222 IV 16 6.25 4 0.250 IV 16.5 8.75 4 0.250 IV 17.75 7.25 4 0.250 IV 18 7.25 4 0.250 IV 21 7.75 4.25 0.235 IV 21.25 7.75 4.25 0.235 IV 22.75 7.5 4.25 0.235 IV 25.5 8.5 4.5 0.222 IV 26 8.25 4.5 0.222 IV 34.5 13.25 4.75 0.211 Mean: 0.237
105
Navicula Sp. a Deep water Apical Axis Transapical Axis Pervalvar axis Stations (μm) (μm) (μm) S/V Ratio 1 16.75 3.5 1.75 0.571 1 17.5 3.75 2.25 0.444 1 18.75 4.25 2.25 0.444 1 19 2.25 2 0.500 1 20.5 4.5 2.5 0.400 1 22 4.25 2 0.500 1 23.25 4.5 2.25 0.444 2 17.25 3.75 2.5 0.400 3 18.75 2 1.75 0.571 3 20.25 4.25 2.25 0.444 3 23.25 4.5 2.5 0.400 3 24.25 4.5 2.5 0.400 4 18.75 4 2 0.500 4 19 4.25 2 0.500 5 17.5 4 2 0.500 5 21 4.25 2 0.500 5 24.5 5 2.75 0.364 6 18.5 2 2 0.500 6 21.5 4.25 2.25 0.444 9 18.5 2 2 0.500 Mean: 0.466 Shallow water Stations IB 15.75 4.5 2.75 0.364 IB 17.75 5 2.5 0.400 IB 15.75 5.25 2.5 0.400 IB 15.5 3.25 2.5 0.400 IB 15.25 4.75 2.5 0.400 IB 14.75 5 2.25 0.444 IB 15.5 5 2.25 0.444 IB 18 5.5 2.25 0.444 IB 15.75 4.5 2.25 0.444 IB 20 3.5 2.25 0.444 IV 15.25 5 2.25 0.444 IV 15.5 4 2.25 0.444 IV 17.5 5.25 2.25 0.444 IV 18 6 2.5 0.400 IV 18.75 5.25 2.75 0.364 IV 19.5 4.5 2.5 0.400 IV 19.5 5 2.5 0.400 IV 20 6.75 2.75 0.364 IV 20 5 2.5 0.400 IV 23 6 2.75 0.364 Mean: 0.411
106
Nitschia frustulum Deep water Apical Axis Transapical Axis Pervalvar axis Stations (μm) (μm) (μm) S/V Ratio 1 6.25 2.5 1.25 0.800 1 7.25 2.25 2 0.500 1 7.5 2.25 1.5 0.667 1 7.5 2.5 2.25 0.444 1 8 2.5 2.5 0.400 1 8.5 2.5 2.5 0.400 1 8.75 2.75 2.5 0.400 2 6.25 2 1.25 0.800 2 8.75 2.75 2.75 0.364 3 6.25 2 1.25 0.800 3 6.75 2.5 1.25 0.800 3 7.75 2.25 2.25 0.444 3 9.5 2.75 2.75 0.364 3 9.5 2.75 2.75 0.364 4 7.5 2.25 2.25 0.444 4 9.25 2.75 2.75 0.364 5 7.25 2.5 2.25 0.444 8 6.5 2 2 0.500 9 9.25 2.75 2.75 0.364 14 7 2 1.25 0.800 Mean: 0.523 Shallow water Stations IB 6 2 1.25 0.800 IB 6.25 2 1.25 0.800 IB 6.5 2 1.25 0.800 IB 7.5 2.25 1.5 0.667 IB 7.5 2.25 1.75 0.571 IB 7.5 2.25 1.75 0.571 IB 7.75 2.25 1.75 0.571 IB 8.25 2.5 1.5 0.667 IB 9 2.5 1.5 0.667 IB 9.5 2.75 2 0.500 IV 6.25 2.5 1.5 0.667 IV 6.25 2 1.25 0.800 IV 6.25 2.25 1.75 0.571 IV 6.75 2.5 1.5 0.667 IV 7.5 2.25 1.75 0.571 IV 7.5 2.25 1.75 0.571 IV 7.75 2.25 1.5 0.667 IV 8.25 2.5 1.5 0.667 IV 8.5 2.5 1.5 0.667 IV 9.25 2.75 2 0.500 Mean: 0.648
107
Nitschia panduriformis Deep water Apical Axis Transapical Axis Pervalvar axis Stations (μm) (μm) (μm) S/V Ratio 1 17.75 7 2.75 0.364 1 30.25 14.25 5.25 0.190 1 31.25 15.25 6.25 0.160 1 31.25 14.75 5 0.200 1 32.75 15.5 5.75 0.174 1 34 17.5 7 0.143 1 34.5 17.25 7 0.143 1 35.5 16.25 6 0.167 3 28 12.75 3.25 0.308 3 30.5 14 4.5 0.222 6 30 14.25 5.75 0.174 7 10.25 4.25 2 0.500 7 29.25 13.75 5.75 0.174 7 32.5 12 5.25 0.190 8 30 16.25 5.5 0.182 8 34.5 13.5 7.25 0.138 14 27.5 13.25 3.5 0.286 14 30.5 16.5 6 0.167 14 33.5 16.5 5.5 0.182 14 34.25 14.75 4 0.250 Mean: 0.216 Shallow water Stations IB 6.25 1.75 1.5 0.667 IB 7.75 2.5 1.25 0.800 IB 9.25 2.5 1 1.000 IB 19.5 7.75 2.75 0.364 IB 19.75 2.75 3.25 0.308 IB 20 7.75 3.75 0.267 IB 22.5 10 3 0.333 IB 25 9.5 3.75 0.267 IB 35 15 4.75 0.211 IB 38 9.5 6.25 0.160 IV 7.5 2.75 1.5 0.667 IV 8 2.25 1.25 0.800 IV 9.5 2.25 1 1.000 IV 19.5 9 2.75 0.364 IV 19.5 8.75 2.75 0.364 IV 21 11.25 2.5 0.400 IV 22.5 7 3 0.333 IV 23.5 10.75 3 0.333 IV 30.25 14.5 4.5 0.222 IV 35.5 15 4.5 0.222 Mean 0.454
108 Appendix P. Taxonomic references. Amphora beaufortiana Hustedt Lit.: Hustedt 1955, p. 38, Pl. 14 fig. 1-5 Lange-Bertalot 2000, p. 131, Pl. 168 Achnanthes brevipes Agardhl fig. 10-11 Lit.: Lange-Bertalot & Krammer 1989, p. 34, Pl. 9 fig. 1-6, Pl. 10 fig. 1-2 Amphora coffeaeformis Agardh Lange-Bertalot 2000, p. 86, Pl. 45 Lit.: Hustedt 1955, p. 39 fig. 1-2 Lange-Bertalot 2000, p.133, Pl. 161 fig. 21-25 Achnanthes conspicua Mayer Lit.: Cleve-Euler 1953, p. 28, fig. 833 Amphora costata W. Smith Lit.: Hendey 1964, p. 264 Achnanthes danica (Flögel) Grunow Lange-Bertalot 2000, p. 134, Pl. 169 Lit.: Lange-Bertalot 2000, p. 274, Pl. 114 fig. 7-14 fig. 5-7
Achnanthes delicatula (Kützing) Grunow Amphora delicatissima Krasske Lit.: John 1983, p. 70, Pl. XXX fig. 3-4 Lit.: Lange-Bertalot 2000, p. 137, Pl. 163 fig. 11-12, Pl. 168 fig. 8 Achnanthes hauckiana Grunow Lit.: Hustedt 1955, p. 17 Amphora exigua Gregory Hustedt 1959, p. 388, fig. 834 Lit.: Hendey 1964, p. 266 Lange-Bertalot 2000, p. 137, Pl. 161 Achnanthes Kolbei Hustedt fig. 15-17 Lit.: Hustedt 1959, p. 397, fig. 846 Amphora granulata Gregory Achnanthes longipes Agardh Lit.: Hustedt 1955, p. 40, Pl. 14 fig. 8-10, Lit.: Hustedt 1955, p. 18 26-27 Lange-Bertalot 2000, p. 92, Pl. 45 fig. 1-12 Lange-Bertalot 2000, p. 139, Pl. 161 fig. 26-27, Pl. 166 fig. 22 Achnanthes manifera Brun Lit.: Hustedt 1955, p. 18, Pl. 6 fig. 1-8 Amphora helenensis Giffen Lit.: Lange-Bertalot 2000, p. 139, Pl. 163 Achnanthes pseudobliqua Simonsen fig. 131-33 Lit.: Lange-Bertalot 2000, p. 94, Pl. 48 fig. 32, Pl. 49 fig. 3 Amphora ovalis Kützing Lit.: John 1983, p. 152, Pl. LXII fig. 11-12 Achnanthes reidensis Foged Lit.: John 1983, p. 75, Pl. XXXII fig. 9-11 Amphora pannucea Giffen Lit.: Lange-Bertalot 2000, p. 146, Pl. 162 Achnanthes taeniata Grunow fig. 23-25 Lit.: Hendey 1964, p. 176 Amphora pseudoholsatica Nagumo & Kobaysi Achnanthes tenera Hustedt Lit.: Lange-Bertalot 2000, p. 148, Pl. 161 Lit.: Hustedt 1955, p. 17, Pl. 5 fig. 22-25 fig. 5-6
Achnanthes tenuis Hustedt Amphora subcuneata Hustedt Lit.: Hustedt 1955, p. 17, Pl. 5 fig. 29-31 Lit.: Hustedt 1955, p. 39, Pl. 14 fig. 17-18
Amphora arenaria Donkin Amphora subturgida Hustedt Lit.: Hustedt 1955, p. 42 Lit.: John 1983, p. 158, Pl. LXVI fig. 9-11 Hendey 1964, p. 268, Pl. XXXVIII fig. 1-4
Amphora tenerrima Aleem & Hustedt Lit.: Hustedt 1955, p. 39, Pl. 14 fig. 15 Lange-Bertalot 2000, p. 152, Pl. 164 fig. 20
109 Amphora ventricosa Gregory Cocconeis disculus Cleve Lit.: Hendey 1964, p. 269, Pl. XXXVIII Lit.: Hendey 1964, p. 178, Pl. XXVIII fig. fig. 12 19 John 1983, p. 156, Pl. LXIV fig. 7-8, LXV fig. Patrick & Reimer 1966, p. 239, Pl. 15 1-10, LXVI fig. 1-2 fig. 1-2 John 1983, p. 77, Pl. XXXIII fig. 10-11 Amphora wisei Salah Lit.: Lange-Bertalot 2000, p. 154, Pl. 162 fig. 18-19 Cocconeis distans Gregory Lit.: Hustedt 1955, p. 17, Pl. 6 fig. 4-5 Anorthoneis tenuis Hustedt John 1983, p. 78, Pl. XXXIII fig. 12-14 Lit.: Hustedt 1955, p. 15, Pl. 5 fig. 14-15 Lange-Bertalot 2000, p. 106, Pl. 38 fig. 12-13 Bacillaria paxillifer (Müller) Hendey var. paxillifer Lit.: Hendey 1964, p. 274, Pl. XXI fig. 5 Cocconeis distantula Giffen Lange-Bertalot 2000, p. 357, Pl. 212 fig. 9-12 Lit.: Lange-Bertalot 2000, p. 107, Pl. 53 fig. 1-2 Biddulphia alternans (Bailey) Van Heurck Lit.: Hendey 1964, p. 102, Pl. XXV fig. 5 Cocconeis granulifera Greville Lange-Bertalot 2000, p. 25, Pl. 7 fig. 6, Pl. 8 Lit.: Greville 1857 fig. 1 Cocconeis hoffmanni Simonsen Biddulphia regina W. Smith Lit.: Lange-Bertalot 2000, p. 109, Pl. 33 Lit.: Hustedt 1930, p. 836, fig. 492 fig. 13, Pl. 14 fig. 13-19
Biddulphia pulchella Gray Cocconeis peltoides Hustedt Lit.: Hendey 1964, p. 101, Pl. XXV fig. 1 Lit.: Hustedt 1955, p. 16 John 1983, p. 36, Pl. XIII fig. 1-3 Hendey 1964, p. 181 Lange-Bertalot 2000, p. 25, Pl. 8 fig. 8-9 Cocconeis pinnata Gregory ex Greville Lit.: Lange-Bertalot 2000, p. 112, Pl. 37 fig. Biremis lucens (Hustedt) Sabbe, Witkowski, & 14, Pl. 39 fig. 10 Vyverman Lit.: Lange-Bertalot 2000, p. 159 Pl. 155 fig. 9-15 Cocconeis placentula Ehrenberg Lit.: Patrick & Reimer 1966, p. 240, Pl. 15 Campylosira cymbelliformis (Schmidt) Grunow ex Van fig. 7 Heurck John 1983, p. 79, Pl. XXXIV fig 11-12, Lit.: Hustedt 1955, p. 13 Pl. XXXV fig. 1 Hendey 1964, p. 157 Lange-Bertalot 2000, p. 26, Pl. 10 fig. 23-25 Cocconeis scutellum Ehrenberg Lit.: Hendey 1964, p. 180, Pl. XXVII fig. 8 Cerataulus radiatus (Roper) R. Ross Lange-Bertalot 2000, p. 114, Pl. 36 fig. Lit.: Hartley 1996, p. 116, Pl. 50 fig. 10 1-7, Pl. 38 fig. 8 Round et al. 1990, p. 234 Cyclotella striata (Kützing) Grunow in Cleve & Cocconeis californica Grunow Grunow Lit.: Lange-Bertalot 2000, p. 102, Pl. 36 Lit.: Hendey 1964, p. 74 fig. 29-30, Pl. 42 fig. 8-15 John 1983, p. 21, Pl. V fig. 10-12
Cocconeis convexa Giffen Cymatosira lorenziana Grunow Lit.: John 1983, p. 76, Pl. XXXIII fig. 1-3 Lit.: Hustedt 1955, p. 13 Lange-Bertalot 2000, p. 27, Pl. 11 fig. 12-15 Cocconeis dirupta Gregory Lit.: Hendey 1964, p. 177 Delphenies karstenii Andrews Lange-Bertalot 2000, p. 105, Pl. 39 Lit.: Lange-Bertalot 2000, p. 45, Pl. 22 fig. 1-5, Pl. 51 fig. 5,8 fig. 9
110 Delphenies surirella (Ehrenberg) Andrews Fallacia forcipata (Greville) Stickle & Mann Lit.: Lange-Bertalot 2000, p. 46, Pl. 22 fig. 7-8 Lit.: Round et al. 1990, p. 554, 668 Lange-Bertalot 2000, p. 205, Pl. 72 Dimeregramma minor (Gregory) Ralfs fig. 2-9 Lit.: Hendey 1964, p. 156, Pl. XXVII fig. 12 John 1983, p. 46, Pl. XVII fig. 4-5 Fallacia litoricola (Hustedt) Mann Lange-Bertalot 2000, p. 29, Pl. 3 fig. 9 Lit.: Round et al. 1990, p. 554, 668 Lange-Bertalot 2000, p. 206, Pl. 71 Diploneis aestuarii Hustedt fig. 7-8, Pl. 72 fig. 31-34 Lit.: Lange-Bertalot 2000, p. 182, Pl. 33 fig. 11-13 Fallacia plathii (Brockmann) Snoeijs Lit.: Lange-Bertalot 2000, p. 210, Pl. 70 Diploneis bombus Ehrenberg fig. 30 Lit.: Patrick & Reimer 1966, p. 416, Pl. 38 fig. 13 Lange-Bertalot 2000, p. 183, Pl. 86 fig. 1-2, Pl. Fallacia vittata (Cleve) Mann 92 fig. 1-3 Lit.: Lange-Bertalot 2000, p. 215, Pl. 70 fig. 21, Pl. 71 fig. 15-16 Diploneis chersonensis (Grunow) Cleve Lit.: Hendey 1964, p. 227, Pl. XXXII Fragilaria brevistriata Grunow fig. 7-8 Lit.: Patrick & Reimer 1966, p. 128, Pl. 4 Lange-Bertalot 2000, p. 184, Pl. 86 fig. 14 fig. 10 John 1983, p. 42, Pl. XVI fig. 1-3
Diploneis decipiens Cleve Fragilaria hyalina (Kützing) Grunow Lit.: Lange-Bertalot 2000, p. 185, Pl. 33 Lit.: Hendey 1964, p. 154 fig. 9-10, Pl. 94 fig. 8 John 1983, p. 43, Pl. XVI fig. 7-10
Diploneis smithii (Brébisson) Cleve Fragilaria pinnata Ehrenberg Lit.: Hustedt 1955, p. 21 Lit.: Hendey 1964, p. 153 Patrick & Reimer 1966, p. 410, Pl. 28 fig. 2 Patrick & Reimer 1966, p. 127, Pl. 4 Lange-Bertalot 2000, p. 193, Pl. 33 fig. 2-5, Pl. fig. 10 89 fig. 1 Fragilaria tabulata (Hustedt) Lange-Bertalot Diploneis vetula Cleve Lit.: Navarro 1982, p. 20, Pl. XIV fig. 11 Lit.: Hustedt 1955, p. 21, Pl. 6 fig. 17-18 Hendey 1964, p. 224, Pl. XXXII, fig. 6 Grammatophora marina (Ralfs) Ehrenberg Lange-Bertalot 2000, p. 196, Pl. 86 Lit.: Hendey 1964, p. 170 fig. 9 Lange-Bertalot, p. 58, Pl. 14 fig. 9-12 Gyrosigma acuminatum Kützing Entomoneis alata (Ehrenberg) Ehrenberg Lit.: Patrick & Reimer 1966, p. 314, Pl. 23 Lit.: Lange-Bertalot 2000, p. 197, Pl. 109 fig. 21-22 fig. 1-3
Entomoneis kjellmanii (Cleve) Poulin & Cardinal Gyrosigma balticum (Ehrenberg) Cleve Lit.: Lange-Bertalot 2000, p. 198, Pl. 173 fig. 12 Lit.: Patrick & Reimer 1966, p. 324, Pl. 25 fig. 1 Eunotogramma marinum W. Smith Hendey 1964, p. 248, Pl. XXXV fig. 9 Lit.: Hustedt 1955, p. 10, Pl. 4 fig. 10-17 John 1983, p. 113, Pl. XLVII fig. 1-3 Lange-Bertalot 2000, p. 32, Pl. 10 fig. 1-3 Gyrosigma beaufortianum Hustedt Lit.: Hustedt 1955, p. 34, Pl. 10 fig. 7-8 Eunotogramma rostratum Hustedt Lit.: Hustedt 1955, p. 10, Pl. 4 fig. 18-22 Gyrosigma fasciola (Ehrenberg) Cleve Lit.: Hustedt 1955, p. 33, Pl. 10 fig. 9 Hendey 1964, p. 248
111 Gyrosigma simile (Grunow) Boyer Navicula diplonoides Hustedt Lit.: Hustedt 1955, p. 34, Pl. 10 fig. 3 Lit.: Hustedt 1955, p. 22, Pl. 8 fig. 21
Lyrella atlantica (A. Schmidt) Mann Navicula directa Cleve Lit.: Round et al. 1990, p. 460, 671 Lit.: Hendey 1964, p. 202 Lange-Bertalot 2000, p. 231, Pl. 96 John 1983, p. 88, Pl. XXXVIII fig. 6 fig. 6, Pl. 98 fig. 5 Lange-Bertalot 2000, p. 275, Pl. 129 fig. 1, Pl. 133 fig. 10-12 Mastogloia angusta Hustedt Lit.: Hustedt 1955, p. 20, Pl. 6 fig. 9 Navicula diversistriata Hustedt Hustedt 1959, p. 512, fig. 940 Lit.: Hustedt 1955, p. 28, Pl. 9 fig. 6-9 Lange-Bertalot 2000, p. 275, Pl. 136 Mastogloia lanceolata Thwaites fig. 1-2 Lit.: Hustedt 1959, pg. 497, fig. 922 Lange-Bertalot 2000, p. 251, Pl. 73 Navicula eidrigiana Carter fig. 6-9 Lit.: Lange-Bertalot 2000, p. 276, Pl. 121 fig. 1-6, Pl. 133 fig. 3-4 Mastogloia pseudoelegans Hustedt Lit.: Hustedt 1955, p. 19, Pl. 6 fig. 10 Navicula eleginesis Gregory Lit.: Patrick & Reimer 1966, p. 524, Pl. 50 Melosira moniliformis (Müller) Agardh fig. 3 Lit.: Hustedt 1930, p. 236, fig. 98 Lange-Bertalot 2000, p. 35, Pl. 1 Navicula ergadensis (Gregory) Ralfs fig. 7-9 Lit. Hendey 1964, p. 216, Pl. XXIX fig. 14-15 Melosira nummuloides Agardh John 1983, p. 90, Pl. XXXVIII fig. 8-9 Lit.: Hendey 1964, p. 72, Pl. 1 fig. 1 Lange-Bertalot 2000, p. 35, Pl. 1 fig. 3-5, 11, 12 Navicula fenestrella Hustedt Lit.: Hustedt 1955, p. 30, Pl. 5 fig. 32 Navicula abunda Hustedt Lit.: Hustedt 1955, p. 27, Pl. 9 fig. 10-12 Navicula formenterae Cleve Lange-Bertalot 2000, p. 265, Pl. 140 fig. 12 Lit.: Hustedt 1955, p. 29, Pl. 7 fig. 28-29 Lange-Bertalot 2000, p. 702, Pl. 130 Navicula agnita Hustedt fig. 32 Lit.: Hustedt 1955, p. 27, Pl. 9 fig. 13-16 Lange-Bertalot, p. 266, Pl. 136 fig. 21, Pl. 142 Navicula Humii Hustedt fig. 10 Lit.: Hustedt 1955, p. 23, Pl. 8 fig. 8-10, 24 Navicula ammophila Grunow Lit.: Hendey 1964, p. 199 Navicula järnfeltii Hustedt Lange-Bertalot, p. 266, Pl. 147 fig. 5-6 Lit.: Patrick & Reimer 1966, p. 486, Pl. 46 fig. 9 Navicula Bastowii Hustedt Lit.: Hustedt 1955, p. 26, Pl. 7 fig. 22-23 Navicula jeffreyi Hallegraff & Burford Lit.: Lange-Bertalot 2000, p. 284, Pl. 142 Navicula cancellata Donkin fig. 37 Lit.: Hendey 1964, p. 203, Pl. XXX fig. 18-20 Navicula menisculus Grunow Lange-Bertalot 2000, p. 271, Pl. 132 fig. 1, Pl. Lit.: Patrick & Reimer 1966, p. 519, Pl. 49 138 fig. 1-3, Pl. 144 fig. 1-7 fig. 17-18 Navicula cincta Ehrenberg Lit.: Lange-Bertalot 2000, p. 272, Pl. 110 fig. 1-29 Navicula nummularia Greville Lit.: Hustedt 1955, p. 22, Pl. 7 fig. 15-16 Navicula digitoconvergens Lange-Bertalot Lit.: Lange-Bertalot 2000, p. 274, Pl. 114 fig. 7-14 Navicula oculiformis Hustedt Lit.: Hustedt 1955, p. 22, Pl. 8 fig. 6-7
112 Navicula palpebralis Brébisson Nitschia calciola Aleem & Hustedt Lit.: Hendey 1964, p. 216, Pl. XXXIV Lit.: Lange-Bertalot 2000, p. 372, Pl. 209 fig. 13-19 fig. 8-10 Patrick & Reimer 1966, p. 540, Pl. 52 fig. 10 Lange-Bertalot 2000, p. 294, Pl. 139 fig. 9, Pl. Nitschia coarctata Grunow 140 fig. 1-3 Lit.: Hendey 1964, p. 278 Lange-Bertalot 2000, p. 374, Pl. 183 Navicula paul-schulzii Witkowski & Lange-Bertalot fig. 13, Pl. 186 fig. 4-13 Lit.: Lange-Bertalot 2000, p. 295, Pl. 141 fig. 19-20, Pl. 145 fig. 16-19 Nitschia constricta Kützing Lit.: Hustedt 1955, p. 45 Navicula pseudolanceolata Lange-Bertalot Lange-Bertalot 2000, p. 377, Pl. 187 Lit.: Lange-Bertalot 1980, p. 32, Pl. 2 fig. 1,3 fig. 8-12
Navicula pullus Hustedt Nitschia frustulum (Kützing) Grunow Lit.: Hustedt 1955, p. 30, Pl. 7 fig. 18 Lit.: Hendey 1964, p. 283 Lange-Bertalot 2000, p. 382, Pl. 209 Navicula reinhardtii Grunow fig. 13-17 Lit.: Patrick & Reimer 1966, p. 517, Pl. 49 fig. 12 Nitschia granulata Grunow Navicula riparia Hustedt Lit.: Hustedt 1955, p. 44 Lit.: Krammer & Lange-Bertalot 1985, p. 92 Hendey 1964, p. 278 John 1983, p. 168, Pl. LXIX fig. 9-10 Navicula rupicola Hustedt Lit.: Hustedt 1961-1966, p. 218, fig. 1335 Nitschia grossestriata Hustedt Lit.: Hustedt 1955, p. 46, Pl. 16 fig. 8-10 Navicula salinarum Grunow Lange-Bertalot 2000, p. 384, Pl. 201 Lit.: Hustedt 1955, p. 27, Pl. 7 fig. 25 fig. 14-16 Hendey 1964, p. 199 Lange-Bertalot 2000, p. 304, Pl. 123 fig. 1-8 Nitschia hybridaeformis Hustedt Navicula Sovereignae Hustedt Lit.: Hustedt 1955, p. 44, Pl. 15 fig. 9-11 Lit.: Hustedt 1955, p. 25, Pl. 8 fig. 18-19 Nitschia incurva Grunow Navicula subhamulata Grunow Lit.: John 1983, p. 169, Pl. LXX fig. 1 Lit.: Patrick & Reimer 1966, p. 495, Pl. 47 fig. 6 Nitschia longa Grunow Navicula submitis Hustedt Lit.: Hustedt 1955, p. 46, Pl. 16 fig. 1 Lit.: Hustedt 1961-1966, p. 128, fig. 1261 Nitschia marginata Hustedt Navicula tripunctata Bory Lit.: Hustedt 1955, p. 46, Pl. 16 fig. 11-12 Lit.: Patrick & Reimer 1966, p. 513, Pl. 49 fig. 3 Nitschia navicularis Grunow Nitschia amphibia Grunow Lit.: Hendey 1964, p. 276, Pl. XXXIX fig. Lit.: John 1983, p. 165, Pl. LXXII fig. 14 3-5 Lange-Bertalot 2000, p. 394, Pl. 184 Nitschia angularis W. Smith fig. 15-18 Lit.: Hendey 1964, p. 281, Pl. XXXIX fig. 6 Lange-Bertalot 2000, p. 368, Pl. 199 fig. 5-6 Nitschia panduriformis Gregory Lit.: Hendey 1964, p. 279 Nitschia brevirostris Hustedt John 1983, p. 172, Pl. LXXII fig. 1-3 Lit.: Hustedt 1955, p. 48, Pl. 16 fig. 21-22 Lange-Bertalot 2000, p. 397, Pl. 184 John 1983, p. 166, Pl. LXIX fig. 5 fig. 13-14, Pl. 186 fig. 1-3
Nitschia Brittoni Hagelstein Nitschia proxima Hustedt Lit.: Hustedt 1955, p. 46, Pl. 15 fig. 7-8 Lit.: Hustedt 1955, p. 46, Pl. 16 fig. 13
113 Nitschia sigma (Kützing) W. Smith Plagiogramma pygmaeum Greville Lit.: Hendey 1964, p. 281, Pl. XLII fig. 1 Lit.: Hustedt 1955, p. 11, Pl. 4 fig. 30-34 John 1983, p. 173, Pl. LXXII fig. 10-11 Lange-Bertalot 2000, p. 404, Pl. 206 fig. 1-10 Plagiogramma Wallichianum Greville Lit.: Hustedt 1955, p. 11, Pl. 4 fig. 29 Nitschia valdestriata Aleem & Hustedt Lit.: Lange-Bertalot 2000, p. 407, Pl. 203 fig. 19-21, Pleurosigma distinguendum Hustedt Pl. 207 fig. 14-16 Lit.: Hustedt 1955, p. 36, Pl. 11 fig. 3-5
Odontella aurita (Lyngbye) Agardh Pleurosigma marinum Donkin Lit.: John 1983, p. 32, Pl. XI fig. 10-11 Lit.: Hustedt 1955, Pl. 11 fig. 2 Lange-Bertalot 2000, p. 36, Pl. 8 fig. 12-13, Pl. Hendey 1964, p. 247, Pl. XXXV fig. 8 9 fig. 1-3 Pleurosigma rostratum Hustedt Odontella rhombus (Ehrenberg) Cleve Lit.: Hustedt 1955, p. 35, Pl. 12 fig. 4 Syn. Biddulphia rhombus Lit.: Hendey 1964, p. 103, Pl. XXV fig. 8 Rhopalodia musculus Kützing Round et al. 1990 p. 220 Lit.: Lange-Bertalot 2000, p. 411, Pl. 214 Hartley 1996, p. 406, Pl. 195 fig. 7-8 fig. 5-8
Opephora marina Gregory Thalassiosira decipiens (Grunow) Jörgensen Lit.: Hustedt 1955, p. 13 Lit.: Hustedt 1930, p. 322, fig. 158 Hustedt 1959, p. 136, fig. 656 Hendey 1964, p. 87, Pl. 1 fig. 5 Hendey 1964, p. 160 Lange-Bertalot, p. 71, Pl. 2-9, fig. 43 Thalassiosira eccentrica (Ehrenberg) Cleve Lit.: John 1983, p. 18, Pl. IV fig. 1-4 Opephora martyi Héribaud Lit.: Hustedt 1959, p. 135, fig. 654 Trachysphinia acuminata Peragallo Patrick & Reimer 1966, p. 115, Pl. 3 fig. 3 Lit.: Hustedt 1955, p. 14, Pl. 4 fig. 50-54 John 1983, p. 50, Pl. XX fig. 3-5 Lange-Bertalot 2000, p. 84, Pl. 24 fig. 17-19 Opephora pacifica (Grunow) Petit Lit.: Hustedt 1955, p. 13, Pl. 4 fig. 47-49 Hendey 1964, p. 159 Lange-Bertalot 2000, p. 72, Pl. 25 fig. 18-26
Opephora schwarzii Grunow Lit.: Hustedt 1955, p. 13, Pl. 4 fig. 46 John 1983, p. 50, Pl. XX fig. 6-7 Lange-Bertalot 2000, p. 73, Pl. 25 fig. 1
Paralia sulcata (Ehrenberg) Cleve Lit.: Hendey 1964, p. 73, Pl. XXIII fig. 5 Lange-Bertalot 2000, p. 37, Pl. 8 fig. 10-11
Paribellus adnatus Cox Lit.: Lange-Bertalot 2000, p. 319, Pl. 104 fig. 16-17
Petroneis latissima (Gregory) Stickle & Mann Lit.: Lange-Bertalot 2000, p. 328, Pl. 100 fig. 4-5
Pinnularia lanceolata Cleve Lit.: Cleve-Euler 1955, p. 21
114 Appendix Q. Deep water diatoms documented as live, and other commonly found species.
PLATE I.
1. Amphora coffeaformis, plain polarized light (l = 23.5 μm) 2. Amphora coffeaformis, plain polarized light (l = 14 μm) 3. Amphora coffeaformis, SEM (scale = 10 μm) 4. Amphora coffeaformis, SEM (scale = 5 μm) 5. Amphora coffeaformis, fig. 4 close-up, SEM (scale = 2 μm) 6. Actinoptychus splendens, plain polarized light (l = 70.75 μm) 7. Actinoptychus splendens, SEM (scale = 20 μm) 8. Actinoptychus splendens, plain polarized light (l = 41.25 μm)
115 PLATE I.
1
2 3 4
5 6
7 8
116
PLATE II.
9. Cocconeis disculus, plain polarized light (l = ~16 μm) 10. Cocconeis disculus, plain polarized light (l = 12 μm) 11. Cocconeis disculus, plain polarized light (l = 17.5 μm) 12. Cocconeis disculus, plain polarized light (l = 15.25 μm) 13. Cocconeis disculus, SEM (scale = 2 μm) 14. Cocconeis disculus, SEM (scale = 5 μm) 15. Cocconeis disculus, SEM (scale = 2 μm) 16. Cocconeis disculus, SEM (scale = 2 μm) 17. Cocconeis disculus, SEM (scale = 2 μm)
117 PLATE II.
10
9 11
12 13 14
15 16 17
118
PLATE III.
18. Cocconeis distans, plain polarized light (l = 37.25 μm) 19. Cocconeis distans, plain polarized light (l = 35.5 μm) 20. Cocconeis distans, SEM (scale = 10 μm) 21. Cocconeis distans, SEM (scale = 10 μm) 22. Cocconeis placentula, plain polarized light (l = 12.5 μm) 23. Cocconeis placentula, SEM (scale = 2 μm) 24. Cocconeis placentula, SEM (scale = 2 μm) 25. Cymatosira lorenziana, plain polarized light (~12 μm) 26. Cymatosira lorenziana, plain polarized light (11.5 μm) 27. Cymatosira lorenziana, inner valve, SEM (scale = 5 μm)
119 PLATE III.
18 19 20
22 23 21
24 25 27 26
120
PLATE IV.
28. Diploneis aestuarii, plain polarized light (l = 13 μm) 29. Diploneis aestuarii, plain polarized light (l = 14.25 μm) 30. Diploneis aestuarii, SEM (scale = 5 μm) 31. Diploneis aestuarii, SEM (scale = 2 μm) 32. Diploneis aestuarii, inner valve, SEM (scale = 2 μm) 33. Diploneis chersonensis, plain polarized light (l = 42 μm) 34. Diploneis chersonensis, SEM (scale = 10 μm)
121 PLATE IV.
28 29
30 31
32 33 34
122
PLATE V.
35. Fallacia forcipata, plain polarized light (l = 24.5 μm) 36. Fallacia forcipata, plain polarized light (l = 32 μm) 37. Fallacia forcipata, plain polarized light (l = 25.75 μm) 38. Fallacia forcipata, SEM (scale = 2 μm) 39. Fallacia forcipata, SEM (scale = 10 μm) 40. Fallacia forcipata, SEM (scale = 5 μm) 41. Fallacia forcipata, inner valve, SEM (scale = 10 μm)
123 PLATE V.
36 37 38 35
39 40 41
124
PLATE VI.
42. Navicula Sp. a, plain polarized light (l = 16.5 μm) 43. Navicula Sp. a, plain polarized light (l = 17.75 μm) 44. Navicula Sp. a, plain polarized light (l = 22 μm) 45. Navicula Sp. a, SEM (scale = 5 μm) 46. Navicula Sp. a, SEM (scale = 5 μm) 47. Navicula digitoconvergens, plain polarized light (l = 18 μm) 48. Navicula digitoconvergens, plain polarized light (l = 26.75 μm) 49. Navicula digitoconvergens, SEM (scale = 5 μm)
125 PLATE VI.
42 43
44 45
45
46 49 47 48
126
PLATE VII.
50. Nitschia frustulum, plain polarized light (l = 8.75 μm) 51. Nitschia frustulum, SEM (scale = 2 μm) 52. Nitschia frustulum, SEM (scale = 2 μm) 53. Nitschia panduriformis, plain polarized light (l = 15 μm) 54. Nitschia panduriformis, plain polarized light (l = 26.5 ) 55. Nitschia panduriformis, plain polarized light (l = 34.25 μm) 56. Nitschia panduriformis, SEM (scale = 2 μm) 57. Nitschia panduriformis, SEM (scale = 10 μm) 58. Nitschia panduriformis, SEM (scale = 2 μm)
127 PLATE VII.
50 51 52
53 54 55
56 57 58
128
PLATE VIII.
59. Nitschia pellucida, plain polarized light (l = 18 μm) 60. Nitschia pellucida, plain polarized light (l = 17.75 μm) 61. Nitschia pellucida, SEM (scale = 5 μm) 62. Nitschia pellucida, SEM (scale = 5 μm)
129 PLATE VIII.
59 60 61 62
130 BIOGRAPHICAL SKETCH
Dorien K. McGee was grew up a coastal girl, living in Savannah, Georgia and Charleston, South Carolina for the majority of her life. She moved inland to Atlanta and graduated with an A.A. from Oxford College of Emory University in 2001 and a B.S. in Environmental Studies from Emory College of Emory University in 2003. There, she supplemented her general environmental background with as much marine science as possible, and spent the summer of 2002 working as a vessel assistant on the NOAA ship FERREL. In the fall of 2003, she began the Masters in Geology program at the University of North Carolina at Wilmington, focusing on marine science and becoming involved with the Coastal Ocean Research and Monitoring Program. She also obtained open water and nitrox SCUBA certifications and quickly became addicted to life underwater. Dorien’s research interests include all things salt water, though coral reef paleontology and biological oceanography have become her passions. She completed a two-year independent study on Pleistocene fossil coral reefs of San Salvador Island, The Bahamas in 2004, presenting her results at the Southeastern Geological Society of America meeting in Memphis, Tennessee in 2003, the annual Geological Soceity of America meeting in Seattle, Washington in 2003, and the 12th Symposium on the Geology of the Bahamas and Other Carbonate Regions on San Salvador Island, The Bahamas in 2004. Her research on deepwater benthic diatoms in Onslow Bay has been presented at the annual Aquatic Sciences meeting of the American Society for Limnology and Oceanography in Salt Lake City, Utah in 2004 and at the UNCW Interdisciplinary Graduate Student Symposium in 2005. She is a member of the Geological Soceity of America, the American Institute of Professional Geologists, the American Society for Limnology and Oceanography, the Association for Women Geoscientists, and the Sigma Xi and Lambda Alpha honor societies. After completing her thesis, Dorien moved to Tampa, Florida to begin a doctoral degree in the Department of Geology at the University of South Florida. Her ultimate goal is to follow her uncle’s footsteps and teach geology on the college level.
131